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BANISTERIA 


A JOURNAL DEVOTED TO THE NATURAL HISTORY OF VIRGINIA 


Problema bulenta (Boisduval & LeConte) 


The status of the two known Virginia populations of this rare inhabitant 
of tidal marshes is discussed on pages 20-22 of this issue 


Number 19 ISSN 1066-0712 2002 


BANISTERIA 


A JOURNAL DEVOTED TO THE NATURAL HISTORY OF VIRGINIA 
ISSN 1066-0712 
Published by the Virginia Natural History Society 


The Virginia Natural History Society (VNHS) is a nonprofit organization dedicated to the dissemination of 
scientific information on all aspects of natural history in the Commonwealth of Virginia. Membership in VNHS 
includes a subscription to Banisteria. Annual dues are $15.00 (per calendar year); library subscriptions to Banisteria 
are $30.00. Subscribers/members outside the United States should add $3.00 for additional postage. Checks should be 
made payable to the Virginia Natural History Society. Membership dues and inquires should be directed to the 
Secretary-Treasurer (address, page 2); correspondence regarding Banisteria to one of the co-editors. Banisteria 1s a 
peer-reviewed journal. For additional information regarding the VNHS, including other membership categories, 
consult our website at: http://fwie.fw.vt.edu/vnhs/ 


Editorial Staff: Banisteria 


Co-editors: 


Joseph C. Mitchell, Department of Biology 
University of Richmond, Richmond, Virginia 23173 


Steven M. Roble, Virginia Department of Conservation and Recreation 
Division of Natural Heritage, 217 Governor Street 
Richmond, Virginia 23219 


Associate Editors 


Richard L. Hoffman, Virginia Museum of Natural History 
Martinsville, Virginia 24112 


Alfred G. Wheeler, Jr., Department of Entomology 
Clemson University, Clemson, South Carolina 29634 


Thomas F. Wieboldt, Department of Biology 
Virginia Polytechnic Institute & State University 
Blacksburg, Virginia 24061 


Cover: Rare skipper (Problema bulenta) on swamp milkweed (Asclepias incarnata), photo by Anne C. Chazal. 
Inside back cover: Original drawing by John Banister; provided by Joseph and Nesta Ewan. 


BANISTERIA 


A JOURNAL DEVOTED TO THE NATURAL HISTORY OF VIRGINIA 


Number 19, 2002 


Table of Contents 


Home Range and Movement of the Allegheny Woodrat (Neotoma magister) in Virginia 
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Spiders of the Family Anyphaenidae in Virginia (Arachnida: Araneida) 
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New Records for Stink Bugs in Virginia (Heteroptera: Scutelleridae, Pentatomidae) 
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Second Update to the Survey of Macrolepidopteran Moths near Vontay, Hanover County, Virginia 
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Status of the Rare Skipper (Problema bulenta) in Virginia 
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First Virginia Records for Three Species of Centipeds (Geophilomorpha: Schendylidae) 
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Shorter Contributions 


Spring Dragonfly (Odonata) and Butterfly (Lepidoptera) Fallout at the Chesapeake Bay Bridge-Tunnel 
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Records for Winter Scorpionflies in Virginia (Mecoptera: Boreidae) 


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Miscellanea 

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Virginia Natural History Society 
Officers 


President 


Werner Wieland 
Department of Biological Sciences 
Mary Washington College 
Fredericksburg, Virginia 22401-5358 


(term expires December, 2002) 


Vice President 


Barbara J. Abraham 
Department of Biological Sciences 
Hampton University 
Hampton, Virginia 23668 


(term expires December, 2002) 


Secretary-Treasurer 


Anne C. Lund 
Department of Biology 
Hampden-Sydney College 
Hampden-Sydney, Virginia 23943 


(term expires December, 2004) 


Councilors 


Paul Bedell 
10120 Silverleaf Terrace 
Richmond, Virginia 23236 


(term expires December, 2004) 


Joella C. Killian 
Department of Biological Sciences 
Mary Washington College 
Fredericksburg, Virginia 22401-5358 


(term expires December, 2002) 


Thomas J. McAvoy 
Department of Entomology 
Virginia Polytechnic Institute and State University 
Blacksburg, Virginia 24061 


(term expires December, 2004) 


Honorary Councilors 


Richard L. Hoffman 
Michael Kosztarab 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


Home Range and Movement of the 
Allegheny Woodrat (Neotoma magister) in Virginia 


Michael T. Mengak’ 


Environmental Science Program 
Ferrum College 
P. O. Box 2383 
Ferrum, Virginia 24088 


INTRODUCTION 


The Allegheny woodrat (Neotoma magister) meets 
the criteria of “species of special concern” in Virginia 
as defined in Terwilliger (1991). The woodrat has been 
extirpated from New York and Connecticut, is 
endangered in New Jersey and Ohio, and is listed as 
threatened in Pennsylvania (Handley, 1991:550). 
Woodrat populations are generally considered to be 
stable in West Virginia and Maryland (Balcom & 
Yahner, 1996), but are declining in Virginia (Mengak, 


2000). Reasons for the loss of some woodrat 
populations and decline in others are unknown. 
Numerous investigators have proposed _ several 
explanations, including habitat fragmentation, 


predation, defoliation of oaks (Quercus spp.) by gypsy 
moth (Lymantria dispar), transmission of a parasite 
from raccoons (Procyon lotor), forest management 
including clearcutting, human disturbance, climate 
change, and food shortage possibly due to increased 
mast utilization by white-tailed deer (Odocoileus 
virginianus) and black bear (Ursus americanus) 
(Handley, 1991; McGowen et al., 1994; Balcom & 
Yahner, 1996). 

Little information is currently available on the home 
range or movements of woodrats in the Ridge and 


Valley Province of the southern Appalachian 
Mountains. This paper reports the results of a short- 
term study of woodrat home _ range _ using 


radiotelemetry. Movement data based on the capture 
and recapture of marked individuals are also presented. 


STUDY AREAS 


The results presented here are from two sources. 


'Present Address: Warnell School of Forest Resources, 


University of Georgia, Athens, GA 30602 
Email: mmengak @smokey.forestry.uga.edu 


The first is radiotelemetry data collected from collared 
woodrats. The study site was located approximately 11 
km north of Callaway, Franklin County, Virginia on 
State Route 744. The Callaway site is atypical for 
woodrat habitat. Typical woodrat habitat consists of 
caves, cliffs, boulder fields, talus slopes and rock 
outcrops. The second source is from trapping data 
collected over 11 years from two sites in Giles and Bath 
counties, Virginia. 

The Callaway site (37°06’N, 80°02’W) was 
privately owned and _ consisted of numerous 
anthropogenic structures including, a house foundation 
(the house was destroyed by fire several years prior to 
this study), an abandoned sawmill with several sawdust 
and sawed board piles, two abandoned vehicles, and 
two sheds. The area encompassed approximately 2 ha. 
The center of the study area was an old field that had 
not been grazed or mowed for approximately 4 years. 
Vegetation in the field was typical for this area — 
blackberry (Rubus spp.), honeysuckle (Lonicera 
japonica), pokeberry (Phytolaca americana), grasses 
and numerous annual and perennial species. Along the 
edge of the field, vegetation consisted of red and white 
oaks (Quercus spp.), pine (Pinus spp.), maple (Acer 
spp.), hickory (Carya spp.), cherry (Prunus spp.), beech 
(Fagus spp.) and other species with oaks and pines 
most abundant. The area was bordered on the east by a 
county maintained dirt road, on the south by a pasture 
grazed by dairy cattle, on the west by forest and a small 
first-order stream and on the north by forest. Several 
occupied houses and barns were within 1.0 km of the 
site. The sawmill had been abandoned for over 3 years. 
Elevation was 400 m. 

The Giles County site (37°22’N, 80°37’W) was 
located approximately 15 km west of Mountain Lake. 
Elevation was 1300 m with a western exposure. The 
site consisted of a long cliff and talus field extending 
for over 800 m in a north-south direction. Tree 
vegetation varied from mountain ash (Sorbus 


4 BANISTERIA 


americana), black birch (Betula lenta) and mountain 
maple (Acer pennsylvanicum) along the northern end to 
northern red oak (Quercus rubra), hickory, and 
sourwood (Oxydendrum arboreum) along the southern 
end. Understory vegetation included blueberry 
(Vaccinium spp.), mountain laurel (Kalmia latifolia), 
greenbrier (Smilax spp.), moss, and ferns and seedlings 
of the dominant trees. 

The Bath County site (38°10’N, 79°45’W) was 
located along an unnamed ephemeral tributary of the 
Jackson River approximately 30 km north of Warm 
Springs, Virginia. The site was a deep cove with an 
eastern exposure. The cove was ringed with cliffs and 
caves along the top edge of the ridge. Tree vegetation 
consisted of white pine (Pinus strobus), eastern 
hemlock (Tsuga canadensis), basswood (Tilia 
americana), shagbark hickory (Carya ovata), northern 
red oak, and white oak (Q. alba). Understory vegetation 
included greenbrier, tree seedlings, mountain laurel, 
and numerous perennial herbs. Elevation was 680 m. 


MATERIALS AND METHODS 


At all three sites, woodrats were live captured using 
single-door, collapsible Tomahawk traps (No. 201) 
baited with apples. Captured animals were ear-tagged 
using No. 1 Monel sequentially numbered ear tags. 
Captured animals were weighed, sexed, examined for 
general body and reproductive condition, aged based on 
weight and pelage condition, and released at the capture 
site. Trapping occurred at numerous intervals 
throughout the year but the exact frequency varied due 
to weather conditions and other factors. Both the Giles 
and Bath county sites have been trapped at least 25 
times between 1990 and 2000. Traps were placed at 
permanently numbered stations. Stations were located 
on a base map of each area and both station number and 
animal number were recorded at each capture. The 
Callaway site was trapped regularly from 1991 to 1993, 
sometimes at 2-week intervals but generally once per 
month. 


Telemetry 


Animals at the Callaway sites were fitted with radio 
collars placed around the neck and secured with a wire 
collar (A. C. Hicks, New York Department of 
Environmental Conservation, pers. comm.). The 
antenna trailed behind the animal. Hollow Hill Systems, 
Ontario, Canada, manufactured the radio collars. 
Collars weighed approximately 15 g, radio frequency 
was 150 MHz, battery life was estimated at 4-5 months, 
and range was estimated at 250-300 m (estimates 
provided by manufacturer). Tracking occurred from 


No. 19, 2002 


January through May 1993. Tracking took place from 
0.5 h before sunset to midnight at least twice per week. 

Animals were located by determining the direction 
from the observer to the animal along the line of the 
strongest audible radio signal. Compass bearings were 
taken from the telemetry station to the animal. 
Telemetry stations were established along the county 
road and at several locations within the field. Stations 
were surveyed with a tape and compass and located on 
a map of the area that included dominant landmarks, the 
road, buildings, a power line and intersections of the 
road with the power line, stream and driveways. 

Telemetry readings were taken once per hour and at 
least three readings were taken on each animal per 
night. Time between readings on an individual could 
be kept to 8 minutes or less because the area was small. 
An attempt was made to locate each animal every hour. 
Since I was able to get relatively close to where the 
animals were located (generally within 30 m), I 
assumed signal bounce was not a factor and therefore 
no corrections were made to the compass readings. 
Readings were plotted on a map of the study area. 
Locations were accepted if they formed a triangle and if 
each leg of the triangle was 5 m or less in length. The 
animal was then assumed to be at the center of that 
triangle. A point, representing the animal’s location was 
placed on the map and the points were connected using 
the Minimum Area Method to determine the home 
range. A dot grid was used to determine the area of the 
home range for each animal. Home ranges were 
determined by month and a home range was calculated 
based on all readings taken on an animal during each 
month. Monthly home ranges were determined only if 
there were a minimum of five acceptable readings for 
an animal during the month. 


Trapping 


Repeated captures of tagged individuals were used 
to determine home ranges at the sites in Giles and Bath 
counties sites. Only animals caught at a minimum of 
three different trap stations and a minimum of 60 days 
between first and last capture were used in this analysis. 
Home range was determined by plotting all capture 
locations on a map of the study area. The outermost 
trap stations were connected using the Minimum Area 
Method. A dot grid was used to compute home range 
size. I also computed a linear measure of movement. I 
defined furthest distance moved between locations as 
the distance between the two furthest trap stations 
where an animal was caught. This was determined by 
measuring, on a map of the study area, the straight-line 
distance between the most distant stations where the 
animal was caught. This measure gives insight into 


MENGAK: ALLEGHENY WOODRAT 5 


short-term movements of woodrats, presumably while 
foraging or seeking mates. 

Neither capture records nor telemetry data give a 
complete accounting of the area used by woodrat. 
However, both methods provide a minimum estimate of 
home range size. Since I did not quantify habitat 
features, no inferences are made regarding habitat use 
versus availability. 

All animals used in the analysis are independent of 
each other. Mean home range size was compared 
between months and between males and females using 
a Student’s t-test. Statistical significance was set at 
a < 0.05 unless otherwise noted. 


RESULTS 
Telemetry 


From 12 January 1993 to 30 April 1993, five 
woodrats (4 females, 1 male) were equipped with radio 
transmitters. Two animals were monitored in January, 
five in February and March, and three in April and 
May. Woodrats at the Calloway sawmill site moved 
very little on cold January nights, preferring to remain 
in their shed or woodpile. Individuals had very small 
home ranges. The individual monthly home range 
varied from 0.003 ha to 0.041 ha. Over four months, 
the individual composite home range varied from 0.021 
ha to 0.105 ha (Table 1). Average home range size for 
the four females during the study was 0.179 ha (SE = 
0.003 ha). 

Movements increased in February perhaps in 
relation to the onset of the breeding season. Radio 
number 131 was a male who lived most of the winter in 


the sawmill and had a home range overlapping three 
females (No. 150, No. 89 and ear tag 207). Not 
surprising, he had the largest home range in both March 
and April and the largest composite home range. He 
was radio-tracked beginning in February and was 
visually observed (in February) mating with a radio- 
collared female over 125 m from the sawmill that was 
in his normal home range. His last known location was 
a burned house foundation 15 m from the shed housing 
female number 70. On 21 May 1993, traps were set at 
the location of the strongest radio signal but he was not 
captured and his fate is unknown. 

One adult female (No. 110) was tracked from 
January to March. Near the end of March, I obtained 
radiolocations indicating that she moved 150-175 m 
north along a small stream. Subsequent tracking lead 
me to believe she was not moving. A ground search 
located her remains (a tooth, fur, partial tail and radio 
collar). Presumably she was killed and eaten by a 
predator (owl, fox and feral cats are known to inhabit 
the area). 

Radio number 150 was a small female (250 g) who 
lived all winter near the sawmill under 2-3 woodpiles. 
Her composite home range was the second largest 
among the four females (Table 1). She remained near 
the woodpiles until April when the landowner used a 
bulldozer to move the woodpiles. Female 150 
temporarily moved to a woodpile 30 m away and just 
inside the woodlot that had been selectively logged in 
March 1993. Her last radio location was taken in late 
May and she had moved at least 0.7 km away, crossing 
three small streams and steep hills. Traps were set near 
where the radio signal was located but she was never 
captured. Her fate was unknown. 


Table 1. Calculated monthly home range (hectares) and number of plotted locations (in parenthesis) of five radio- 
collared adult Allegheny woodrats in Franklin County, Virginia, 1993. 


Animal Number 


Month 70(Q) 89(Q) 110(9) 150(Q) 131(d) 
January 0.005 ( 9) wt 0.009 (10) es a, 

February 0.032 (17) 0.045 (14) 0.015 (7) 0.033 (12) 0.015 (12) 
March 0.013 (18) 0.021 (15) 0.003 (12) 0.015 (18) 0.044 (17) 
April 0.003 (10) 0.0287 (9) oa" 0.011 ( 8) 0.041 (7) 
Composite HR 0.037 (34) 0.069 (29) 0.021 (17) 0.054 (30) 0.105 (29) 


' Not collared until late January or early February. 


* Lost her collar in early April. 


> Round dead in March. 


6 BANISTERIA 


Three animals remained in May 1993 (radio 
numbers 70, 131 and 150) and tracked to determine a 
final location before tracking ended and the batteries 
expired. Animal 70 had not appeared to move from 
under a shed for 3-4 weeks in late-April and early-May 
and was presumed to have died. A large ear-tagged 
male (410 g, tag 222/238) was caught five times in the 
shed where female 70 lived all winter. 


Trapping — Giles County 


Ten individuals were caught at least three times but 
at only two stations and could not be included in the 
home range analysis. Nineteen individuals were caught 
at least three times and at a minimum of three stations 
over the 11-year study. Ten were females and nine 
were males. The age (at first capture) distribution was: 
females-5 adults, 2 juveniles, and 3 subadults; males — 
8 adults and 1 juvenile. All age categories were 
combined within gender for the analysis. 

Mean number of captures was 9.1 and 6.2 times for 
females and males, respectively (Table 2). The longest 
distance moved between any two trap stations was by a 
female (No. 334) and covered a distance of 340 m. 
This movement occurred between two capture events 
only 66 days apart. In contrast, another adult female 
was trapped 11 times over nearly four years (Mengak 
1997). Her greatest linear movement between any two 
captures was only 50 m but the captures were 457 days 
apart (8 July 1994 and 15 October 1995). The longest 
distance between any two captures was 340 m and 310 
m for females and males, respectively. 

Average distance between the furthest two capture 
locations was 169.7 m (SD = 108.3 m) and 190.6 m 
(SD = 92.3 m) for females and males, respectively. 
The difference was not significant (t = -0.440, df = 17, 
P < 0.05) 


No. 19, 2002 


Home range size based on trapping observations 
was 0.189 ha (SD = 0.136 ha) for females and 0.234 ha 
(SE = 0.202 ha) for males. The difference was not 
statistically different (t = -0.546, df = 12, P < 0.05). 


Trapping — Bath County 


Thirteen individuals were caught three or more 
times but only at two trap stations and were excluded 
from further analysis. Nineteen individuals were used 
in the analysis — 14 females and 5 males. The age 
distribution (at first capture) for females was: 6 adults, 
5 juveniles, and 3 subadults. The age distribution for 
males was | adult, 2 juveniles, and 2 subadults. Once 
again, all age categories were combined for analysis. 

The longest distance between any two captures was 
245 m and 180 m for females and males, respectively. 
The average distance between the furthest two capture 
locations was 102.1 m (SD = 68.8 m) and 104.0 m (SD 
= 68.1 m) for females and males, respectively. The 
difference was not significant (t = 0.012, df = 16, 
P < 0.01). 

Home range size based on trapping observations 
was 0.068 ha (SD = 0.084 ha) for females and 0.063 ha 
(SE = 0.049 ha) for males. The difference was not 
statistically different (t = 0.134, df =16, P < 0.05). 


DISCUSSION 


Telemetry and trapping provided insights into the 
behavior of individual woodrats. At the Callaway site, 
the relationship between female 110 (collared) and 
female 209 (uncollared) is particularly interesting. 
Female 209 inhabited an abandoned car and shed in 
March/April 1992. Her last capture was on 23 April 
1992. Female 110 was first caught near the abandoned 
car in September 1992 and repeatedly caught in the car 


Table 2. Summary of measures (mean and standard deviation) used to assess movement of Allegheny woodrats in 
Virginia based on capture and recapture records, 1990-2000. 


Mean Mean 
Number of Number of Home 
Individuals Captures Range (ha) 
Giles County 
Females 10 9.1 (2.6) 0.189 (0.136) 
Males 9 6.2 (3.2) 0.234 (0.202) 
Bath County 
Females 14 10.4 (5.1) 0.068 (0.085) 
Males ) 8.5 (4.1) 0.063 (0.049) 


Longest distance 
moved between 
any 2 captures (m) 


Days between 
first and 
last capture 


169.7 (108.3) 596.6 (285.6) 


190.6 (92.3) 512.1 (383.9) 
102.2 (68.8) 429.5 (283.6) 
104.0 (68.1) 312.8 (199.1) 


MENGAK: ALLEGHENY WOODRAT vi 


and shed through March 1993. Upon the death of 
animal 110 in late March, female 209 was again caught 
in the shed within 10 days of telemetry indicating that 
No. 110 had moved upslope along the stream to the site 
where she was found dead. It is assumed that 110 
displaced 209 and occupied the area until her death. 
Woodrat 209 probably existed in the woods and brush 
piles near the car and shed but was never captured again 
until 110 was removed from the area. This raises 
questions concerning the apparent disappearance from 
the trappable population of other woodrats and leads me 
to suspect that displaced animals may exist on the 
fringe of the trap area. 

Both eastern (N. floridana) and Allegheny woodrats 
are known to cache food items in autumn for 
overwinter use (Poole, 1940; Fitch & Rainey, 1956). 
Large food caches were obvious in several of the 
buildings known to house radio-collared individuals. 
Cached food items comprise the primary food supply 
during winter (Castleberry, 2000a) but limited foraging 
occurs presumably during periods of favorable weather. 
Caching allows access to food throughout the winter 
with minimal exposure to harsh weather or predators. 
The availability of cached foods helps explain the small 
home range size as determined by telemetry at the 
Callaway site. 

Movements based on trapping records showed little 
pattern. Some animals made long movements, others 
moved very little. Sometimes the maximum movement 
occurred over a relatively short time interval. At other 
times, the animal was caught several times over many 
months but always at about the same trap station. Of 
course, there is no way to know the movements of the 
animals between trapping events. The data presented 
here suggest that, over time, most woodrats move 
relatively little. They may move larger distances but 
they seem to return to a “central” location where they 
are most often trapped. 

Although males seem more likely to move longer 
distances over the total number of capture events, there 
is very little difference between males and females 
when considering distance moved between any two 
consecutive dates. This could mean that both males and 
females make considerable exploratory movements for 
feeding or breeding but males may travel further than 
females. This observation may receive support from the 
home range data on radio-collared woodrats, but only 
one male was radio tracked so the data are clearly 
incomplete at this time. 

Zuck (Department of Forestry, West Virginia 
University, pers. comm.) used radio telemetry to assess 
juvenile dispersal of woodrats in West Virginia. 
During 1999-2000, they did not observe any juvenile 
dispersal. However, an ear-tagged male was recaptured 


approximately 2 km from his original capture site and 
other individuals were reported to have made 
movements > 400 m for their original capture location 
(range 500-2500 m). Castleberry et al. (2001) estimated 
spring and summer home range size of 34 radio- 
collared Allegheny woodrats as 6.5 ha and 2.2 ha for 
males and females, respectively. Castleberry et al. 
(2001) studied movements in relation to timber 
management and found that home range varied within 
timber harvest treatment from 1998 to 1999. For 
example, in clearcut areas, home range was 6.0 ha and 
2.2 ha for all individuals in 1998 and 1999, 
respectively. Other treatments showed — similar 
differences between the two years. Maximum nightly 
distance moved from the den during foraging forays 
ranged from 134.5 m to 186.4 m. These distances are 
similar to the trapping results in my study. 

Castleberry et al. (2001) pointed out that their home 
range results are larger than any reported for most other 
Neotoma species. They suggested that home ranges are 
generally larger in spring and summer when the animals 
are actively foraging and seeking mates. Mengak 
(2002) found that most woodrat reproduction occurs in 
March-May in Virginia. Castleberry (2000b) failed to 
detect any influence of moon phase or illumination on 
the activity patterns of woodrats in his study. 
Castleberry et al. (2001) found that woodrats used 
forest and clearcut areas in proportion to their 
availability. 

In my study, the Bath County site consisted of intact 
forest but the Giles County site had intact forest, open 
talus with no overstory and edge habitat along a field 
border. The juxtaposition of various habitat types 
(including the old field at the Callaway site) does not 
seem to negatively affect patterns of woodrat 
movements. Woodrats were caught in traps in the old 
field and in the open talus field, as well as under the 
forest canopy. Timber type, harvest activity, or edges 
do not seem to inhibit woodrat movements nor exclude 
woodrats from an area. Other environmental factors, 
such as food supply and competition, predation or 
disease, may have a greater impact on woodrat 
distribution, habitat occupancy, and colony persistence 
than human activity. 

In conclusion, Allegheny woodrats in this study 
have small winter home ranges as determined by 
telemetry. Trapping results, though providing a small 
sample, seem to confirm that at my study sites across 
multiple years, individual resident woodrats are 
generally caught within a small area of the larger 
habitat. Because of the multiple years covered by this 
study, no information is available on home range 
overlap or territorial behavior. Small home ranges and 
the isolated nature of suitable woodrat habitat make this 


8 BANISTERIA 


species very vulnerable to local extinctions. Issues 
related to recolonization of extirpated habitat and 
juvenile dispersal (and gene flow) remain unanswered 
but vital to a thorough understanding of woodrat 
ecology in Virginia and throughout the range. 


ACKNOWLEDGMENTS 


Fieldwork for this project was supported by the 
Pittman-Robertson Federal Aid to Wildlife Restoration 
Project-WE99R and the Virginia Department of Game 
and Inland Fisheries (VDGIF) Nongame Program, 
USFS George Washington/Jefferson National Forests 
(USFS GW/Jeff) and Ferrum College Life Science 
Division. S. Griep (USFS GW/Jeff) and R. Reynolds 
(VDGIF) provided funding, logistical support, and 
many helpful comments on this project. Funds for data 
analysis and manuscript preparation were provided by a 
summer fellowship from the Appalachian College 
Association. Numerous students in the Environmental 
Science Program at Ferrum College assisted with 
fieldwork throughout the study. 


LITERATURE CITED 


Balcom, B. J. & R. H. Yahner. 1996. Microhabitat and 
landscape characteristics associated with the threatened 
Allegheny woodrat. Conservation Biology 10: 515- 
D205; 


Castleberry, N. L. 2000a. Food habits of the Allegheny 
woodrat (Neotoma magister). M.S. Thesis, West 
Virginia University, Morgantown, WV. 98 pp. 


Castleberry, S.  B.  2000b. Conservation and 
management of the Allegheny woodrat in the Central 
Appalachians. Ph.D. Dissertation, West Virginia 
University, Morgantown, WV. 166 pp. 


Castleberry, S. B., W. M. Ford, P. B. Wood, N. L. 
Castleberry, & M. T. Mengak. 2001. Movements of 


No. 19, 2002 


Allegheny woodrats in relation to timber harvesting. 
Journal of Wildlife Management 65: 148-156. 


Fitch, H. S., & D. G. Rainey. 1956. Ecological 
observations on the woodrat, Neotoma_floridana. 
University of Kansas Publications, Museum of Natural 
History 8: 499-533. 


Handley, C. O., Jr. 1991. Mammals. Pp. 539-616 In 
K. Terwilliger (coordinator). Virginia’s Endangered 
Species. McDonald and Woodward Publishing 
Company, Blacksburg, VA. 672 pp. 


McGowan, E. M., A. C. Hicks, & W. B. Stone. 1994. 
Evidence implicating Baylisascaris procyonis in the 
extirpation of the Allegheny woodrat from New York 
State. Proceedings of The Wildlife Society, First 
Annual Conference, Albuquerque, NM. (Abstract). 


Mengak, M. T. 1997. New field records for longevity 
in Allegheny woodrats (Neotoma magister). Banisteria 
10: 27-28. 


Mengak, M. T. 2000. Status and distribution of the 
Allegheny woodrat (Neotoma magister) in Virginia. 
56" Northeast Fish and Wildlife Conference, 
Charleston, WV. (Abstract). 


Mengak, M. T. 2002. Reproduction, juvenile growth 
and recapture rates of Allegheny woodrats (Neotoma 
magister) in Virginia. American Midland Naturalist 
148: in press. 


Poole, E. L. 1940. A life history sketch of the 
Allegheny woodrat. Journal of Mammalogy 21: 249- 
270. 


Terwilliger, K. 1991. Introduction. Pp. 3-7 In 
K. Terwilliger (coordinator) Virginia’s Endangered 
Species. McDonald and Woodward Publishing 
Company, Blacksburg, VA. 672 pp. 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


Spiders of the Family Anyphaenidae in Virginia 
(Arachnida: Araneida) 


Richard L. Hoffman 


Virginia Museum of Natural History 
Martinsville, Virginia 24112 


Anyphaenids (which have no “common” name) 
are small, pallid, ground-dwelling spiders, generally 
widespread in distribution but infrequently collected 
either by hand or with pitfall traps. North American 
species of the family were revised about three decades 
ago (Platnick, 1974), so that accurate identifications can 
be made with some confidence. A better knowledge of 
the family in different parts of its range now awaits only 
the accretion of relevant study material. 

Examination of the distribution maps in Dr. Platnick's 
monograph suggests that 11 species should occur in 
Virginia, and intensive collecting activity during the past 
decade by personnel of the Virginia Museum of Natural 
History (VMNH) and the Division of Natural Heritage, 
Virginia Department of Conservation and Recreation 
(VDNH), has secured identifiable specimens of all but 
one of them. The northernmost locality of the fugitive 
species, Hibana velox, is in north central North Carolina, 
and the spider almost certainly occurs in southside 
Virginia. However, the surprising discovery of Hibana 
cambridgei in Virginia opens the possibility that any or all 
of the several anyphaenids known only from Florida, for 
instance, might also be found here. 

Since most of our species are known from only a few 
captures (the one most frequently taken is known from 
only 12 sites), it will obviously be a long time before we 
can claim an even superficial knowledge of temporal and 
spatial distributions of these little spiders in Virginia. 
However, the data at hand suggest that several species 
occur statewide, and some may be restricted to the Coastal 
Plain. So far no species seem to be endemic to the western 
mountainous parts of the state, and none have been taken 
in the Mount Rogers-Whitetop region despite fairly 
prolonged trapping in a variety of habitats. 

Even the limited material at hand suggests an 
interesting biological situation that invites more intentive 
investigation: the sequential - nearly exclusive - periods of 
surface activity by adults of the local sympatric species of 
Anyphaena. Anyphaena celer and A. maculata are Fall- 
Winter species, A. fraterna is most frequently trapped in 


May and June, and A. pectorosa is active almost 
exclusively in July. Perhaps such seasonal displacement 
enhances reproductive isolation, or is useful in resource- 
sharing. The very limited data suggest that the two local 
species of Wulfila may likewise be separated temporally. 

The ready availability of Platnick’s monograph 
obviates the need for maps and illustrations. Users of this 
reference are reminded that many Nearctic species 
traditionally referred to the genus, Aysha have been 
relocated into the new genus Hibana (Brescovit, 1991) 
and the name Wulfila alba was replaced by W. albens 
(Platnick, 1997). Otherwise the nomenclature remains 
stable. 


ANNOTATED LIST 


Collections not otherwise credited were made by 
VMNH personnel either as individuals or as part of 
organized sampling programs. 


1. Anyphaena celer Hentz New state record 


The range of this species is general over eastern 
United States, from Massachusetts and Michigan south to 
Florida, Texas, and Missouri, with the majority of 
recorded localities clustered toward the north. No 
Virginia material was available to Platnick (1974: map 
1), but our records suggest the species occurs statewide. 

Clarke Co.: Blandy Farm, ca. 3 km S Boyce, 
24 August 1991, ex Malaise trap, D. R. Smith (1 CO). 
Henry Co.: Martinsville, inside VMNH building, sticky 
trap, January 1995 (1 0’). Mecklenburg Co.: Elm Hill 
WMA, DF site in mixed woods near Kerr Dam 
powerhouse, 15 March-3 April 1991 (1 ©’); same locality 
but open field DF site by Lake Gaston, 24 February- 
3 April 1996 (4 GC’). Nelson Co.: The Priest, 3900 ft., 
ca. 4.5 mi. SE Montebello, 23 November-12 December 
1991, pitfall trap (1 &). Pittsylvania Co.: DF site ca. 3 
miles ENE Axton, 29 February-29 March 1992 (numerous 
OC). 


10 BANISTERIA 


Apparently this species is psychrophilic, with the 
collection dates falling between late August and early 
April. The only two series were both taken in March. 


2. Anyphaena fraterna (Banks) New state record 


This species is generally distributed over much of 
eastern North America: east of the Great Plains and south 
of glaciated regions, although unknown in peninsular 
Florida. It is probably statewide in Virginia at lower 
elevations, although most records are from east of the 
Blue Ridge. 

VMNH samples are from: Chesterfield Co.: Scotford 
Road, 1.2 km SE ject. Va. Rt. 175 and County Rt. 679, 
May 1994, S. M. Roble (1 G). Essex Co.: 1 mi. S 
Dunnsville, ex Malaise trap, 4-14 May 1993, D. R. Smith 
(several OC’ and QQ). Henrico Co.: west Richmond, 
Derbyshire Road, June 1996, W. H. Mitchell (1 &). Henry 
Co.: Martinsville, inside VMNH building, 4 May 1994, 
C. R. Carter (1 &). King George Co.: Naval Weapons 
Laboratory, Dahlgren, 26 June 1991, K. A. Buhlmann, 
VDNH (1 @). Roanoke Co.: Back Creek District, Bandy 
Road, 9 May 1995, M. W. Donahue (1 @). Stafford Co.: 
Quantico Marine Corps Base, Beaver Run, N of Camp 
Barrett, 11 May 1999, A. C. Chazal, VDNH (1 &). York 
Co.: Grafton Ponds, 1 May 1990, K. A. Buhlmann, 
VDNH (1 ©). City of Virginia Beach: Seashore State 
Park, 1 May 1989 (1 &), 26 July 1989 (19), both K. A. 
Buhlmann, VDNH. 

Surface activity, at least by males, is almost entirely 
in May, with only a few June captures. 


3. Anyphaena maculata (Banks) New state record 


Published records suggest a predominantly lowland 
range from Long Island to Louisiana and Arkansas, witha 
small - perhaps disjunct - contingent in the southern 
Appalachians. Our two localities in eastern Virginia are 
consistent with this generalization. 

Chesterfield Co.: Scotford Road, 1.2 km SE jct Va. 
Rt. 175 and County Rt. 679, 6 March 1994, S. M. Roble 
(1 &). Greensville Co.: 1 mi. E Claresville at end of Rt. 
600, 12 November 1993-25 January 1994 (1 C). 

The specimen from Chesterfield County is a little 
atypical in that the median apophysis of the male palpal 
organ is substantially broader than shown for the species 
in Platnick’s revision (1974: Fig. 2), as well as more 
spatulate apically and not extended into a curved tip. In 
other respects there is such overall agreement that this 
departure is considered to be within the normal range of 
variation. 


No. 19, 2002 
4. Anyphaena pectorosa L. Koch 


This spider is generally distributed in eastern United 
States: New York to Michigan, south to Florida and 
Texas. 

The species description in Platnick (1974: 232) is 
based on a specimen from Fairfax County, and A. 
pectorosa has been recorded from alfalfa fields in 
Montgomery County by Howell & Pienkowski (1971). 

VMNH material is from: Essex Co: 1.5 km SE 
Dunnsville, ex Malaise trap, 2 July and 12 July 1991, 
D. R. Smith (5 OO", 2 QQ). Greensville Co.: 1 mi. E 
Claresville, end of Rt. 666, 30 June-15 July 1994 (1 0’). 
Mecklenburg Co.: 2 mi. SE Boydton, 25 June 1990, J.C. 
Mitchell (1 &). Pulaski Co.: Dublin, fen site at Radford 
Army Ammunition Plant, 2 July 1999, S. M. Roble et al. 
VDNH (1 O). 

Capture records, all between mid-June and mid-July, 
suggest a fairly narrow season of surface activity for 
adults of this species, contrasting with the generally much 
earlier season for A. fraterna. 


5. Hibana cambridgei (Bryant) New state record 


As depicted by Platnick (1974: map 4), this species 
ranges from the southern Mexican Plateau north as far as 
Missouri and Alabama. The discovery of H. cambridgei 
in Virginia constitutes a northeastward extension of about 
550 mi/880 km from the location plotted in northern 
Alabama. 

King George Co.: Naval Weapons Laboratory, 
Dahlgren, swale pitfall site, 26 June 1991, K. A. 
Buhlmann, VDNH (1 ©@). 

The male palpal organ of this specimen matches 
Platnick’s illustration (Fig. 120) to the finest detail; there 
can be no doubt of the identification. The spider is, 
however, substantially larger than the individual which he 
described: total length ca. 8 mm, carapace length 3.2 mm. 
(vs. 5.9 and 2.4 mm, respectively). 

Is the Dahlgren population native to Virginia? If so, 
it is either naturally disjunct from the main body of the 
range, or simply occupies a biotope neglected during most 
sampling work and thus likely to be found in the 
intervening area. The possibility suggests itself, however, 
that chance introduction by “military commerce” cannot 
be discounted. The possibly analogous situation involving 
a minute lygaeid bug, Botocudo modestus, may be 
relevant. This insect was known only west of the 
Mississippi River prior to its recent discovery at Wallops 
Island, Accomack Co., Virginia (Hoffman, 1999); this 
locality is occupied by a quasimilitary federal installation. 


HOFFMAN: SPIDERS 11 


Botocudo was not recovered in similar habitat with similar 
trapping techniques over a period of several months at 
Assateague Island, only a few kilometers distant. These 
uncertainties would of course be conclusively resolved by 
the collection of either species at a Virginia site (or 
elsewhere in the central Atlantic states) remote from 
possible contamination through commerce between 
military bases. 


6. Hibana gracilis (Hentz) 


This spider occupies an extensive geographic range, 
from New York and Iowa south to Florida and 
southernmost Texas but records are lacking for most of 
the Appalachian region. It is the anyphaenid most 
frequently collected in Virginia, with specimens at hand 
from eight counties and two cities mostly east of the Blue 
Ridge. Platnick’s range map (1974, map 4) included 
localities in Northampton and Fairfax counties, and 
Virginia Beach City. 

VMNH material is from: Chesterfield Co.: Scotford 
Road, 1.2 km SE jct Va. Rt 175 and County Rt. 679, 22 
April 1995, S. M. Roble (2 3:4). Greensville Co.: 2.3 mi. 
NE Slates Corner, 18 June 1990, J. C. Mitchell (1 9). 
Henry Co.: Martinsville, C. R. Carter (1 3). King George 
Co.: Caledon State Park, 7 June 1993, B. J. Abraham 
(13). Montgomery Co.: Radford, around dwelling, Fall 
1990 (1 @). Pittsylvania Co.: Chatham, 11 March 1999 
(1 2). Roanoke Co.: Salem, Green Hill Park, 20 April 
1995, M. W. Donahue (1 92); York Co.: Grafton Ponds, 
1 May 1990, K. A. Buhlmann, VDNH (1 3). City of 
Chesapeake: Fentress Naval Air Station, 6 June 1989, 
kK. A. Buhlmann, VDNH (3 ¢), and City of Virginia 
Beach: Seashore State Park, 1 May 1989, K. A. 
Buhlmann, VDNH (1 3). 

The great majority of these spiders were collected 
during March, April, and May. Two are from June, and 
only one has an ambiguous “Fall” date. 


[Hibana velox (Becker) | 


A southern species, so far not collected in Virginia 
but surely to be expected in the “Southside” counties 
being represented on Platnick’s distribution map for 
north-central North Carolina (vicinity of Durham?), less 
than 35 miles from the state line. 


7. Oxysoma cubanum Banks New verified state record 


This southern species ranges as far northward as New 
Jersey, and presumably occurs throughout the Coastal 
Plain and outer Piedmont in Virginia, although there are 
only two authentic records: 

Louisa Co.: 4 mi. S Cuckoo, ex Malaise trap, 28 


April-4 May 1986 (2 33); 18-27 May 1986 (1 3,2 29), 
both D. R. Smith. City of Virginia Beach: Oceana Naval 
Air Station, 3 May 1989, K. A. Buhlmann, VDNH (1 <); 
Sandbridge, 11 September 1993, B. J. Abraham (1 Q). 

The published record for alfalfa fields at Blacksburg, 
Virginia (Howell & Pienkowski, 1971) seems 
geographically implausible, and the original material 
cannot be located for verification. 


8. Teudis mordax (O. P.-Cambridge) New state record 


Already documented for North Carolina and the 
District of Columbia by Platnick (1974), this species 
could safely be assumed to reside in Virginia east of the 
Blue Ridge generally. However, so far we have records 
only for two Coastal Plain sites: 

Essex Co.: 1.5 km SE Dunnsville, ex Malaise trap, 

2 July 1991, D. R. Smith (1 3). City of Suffolk: Great 
Dismal Swamp National Wildlife Refuge, 30 June 1993, 
B. J. Abraham (1 @). 


9. Wulfila albens (Hentz) New state record 


Although W. albens occurs from Maryland to Florida 
and Texas, there are apparently no published records for 
the species in Virginia. 

We have only two specimens from the state: 
Cumberland Co.: 5.5 km SSW Columbia, DF site in pine 
woods, 2 September 1990 (1 2); 7 km SSW Columbia, 
DF site in mixed hardwood forest, 1 August 1990 (1 ) 
(both J. C. Mitchell). On the basis of records in nearby 
states, W. albens should be essentially statewide in 
Virginia, at least at lower elevations. 


10. Wulfila saltabunda (Hentz) 


One of the most widely distributed of Nearctic 
anyphaenids, W. saltabunda occurs from Nova Scotia to 
Florida, westward to Minnesota, Iowa, and Texas. Its 
presence in Virginia is attested solely by a record for 
Virginia Beach City, plotted on Map 3 in Platnick’s 1974 
revision, and capture in alfalfa fields at Blacksburg, 
Montgomery County (Howell & Pienkowski, 1971). 
Presumably it should be found statewide. 

Louisa Co.: 4 mi. S of Cuckoo, ex Malaise trap, 6-13 
June 1986, D. R. Smith (2 3). Patrick Co.: roadside on 
Rte. 669, 3 mi. SW Ararat, sweeping Ceanothus, 27 June 
1992 (1 2). 


ACKNOWLEDGMENTS 
The material accumulated during VDNH surveys was 


donated to VMNH by staff zoologists Christopher A. 
Pague and Steven M. Roble. Appreciation is also 


12 BANISTERIA 


expressed to Dr. Roble, and to Joseph C. and Wendy H. 
Mitchell, David R. Smith, Barbara J. Abraham, and 
Michael W. Donahue for the gift of specimens generated 
during their personal collecting activities. 


LITERATURE CITED 
Brescovit, A.D. 1991. Hibana, novo género de aranhas 
da familia Anyphaenidae (Arachnida, Araneae). Revista 
Brasileira de Entomologia 35: 729-744. 


Hoffman, R. L. 1999. Six species of bugs new to the 
Virginia list (Heteroptera: Coreidae, Lygaeidae, 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


No. 19, 2002 
Phymatidae, Miridae). Banisteria 14: 24-28. 


Howell, J. O., & R. Pienkowski. 1971. Spider populations 
in alfalfa, with notes on spider prey and effect of harvest. 
Journal of Economic Entomology 64: 163-168. 


Platnick, N. I. 1974. The spider family Anyphaenidae in 
America north of Mexico. Bulletin of the Museum of 
Comparative Zoology 146: 205-266. 


Platnick, N. I. 1997. Advances In Spider Taxonomy 
1992-1995. New York Entomological Society. 976 pp. 


New Records for Stink Bugs in Virginia 
(Heteroptera: Scutelleridae, Pentatomidae) 


Richard L. Hoffman 


Virginia Museum of Natural History 
Martinsville, Virginia 24112 


Three decades have passed since publication of my 
survey (1971) of the pentatomoid Heteroptera in “The 
Insects of Virginia” series, during which time our 
knowledge of these insects has been substantially 
increased. Six species were added to the state list, and a 
number of recent name changes noted some years ago 
(Hoffman, 1994); it is now desirable to present a sequel 
that adds still another pentatomid to our fauna and 
provides significant distributional records for several 
others. 

The occasion is taken to offer a key to the Virginia 
genera of the subfamily Asopinae, not recognized in my 
1971 treatment, and another to our species of Podisus 
which accommodates the additional member of this genus 
here documented as native to the state. 

Unless otherwise specified, the material mentioned 
herein is located in the Virginia Museum of Natural 
History (VMNH), which is under ongoing obligation to 
the staff of the Division of Natural Heritage, Virginia 
Department of Conservation and Recreation, for donation 


- through the interest of Steven M. Roble - of valuable 
material obtained during its inventory activities around 
the state. The classification and nomenclature follows that 
of Froeschner (1988), except as specifically noted. 


FAMILY SCUTELLERIDAE 
Camirus porosus (Germar) 


Although this northern member of a mostly 
Neotropical genus is virtually continent-wide in North 
America, actual capture records are rare and only a few 
states can claim C. porosus as a native resident. A 
collection from beach drift at Virginia Beach (Jones, 
1935) provided the northernmost locality in eastern 
United States, and this tenuous evidence has to my 
knowledge never subsequently been verified. There is 
always some ambiguity about the origin of any beach drift 
finds, there being usually no way to know from what 
locality a specimen actually entered the water. 


HOFFMAN: STINK BUGS 13 


It is now possible to document an unequivocal 
Virginia locality for this very rare species: Nottoway Co.: 
Fort Pickett Military Reservation, 1.6 mi. E jct. Wilcox 
and Range roads, 7 July 1999, Anne C. Chazal and Amber 
K. Foster, VDNH survey (1). In addition to providing the 
new northernmost known locality for C. porosus, this site 
is of interest for its inland position on the Virginia 
Piedmont rather than in the Coastal Plain as might have 
been expected. 

At first glance, C. porosus bears a considerable 
resemblance in size, shape, and coloration to species of 
the genus Galgupha, except that the integument is matte 
instead of shiny. A good dorsal habitus illustration was 
published by Froeschner (1988), but it does not indicate 
the coarse, dense punctation of the entire body. As seen 
with magnification, the bug has an unprepossessing facies 
with its dull black coloration, small eyes, and large, 
declivous head which is retracted up to the eyes in the 
prothorax (Figs. 1A, 1B). An interesting feature is the 
accommodation of the long antennae in the deep, narrow, 
prothoracic rostral groove from which, in the preserved 
specimen, they had to be extracted with a fine needle. 
This groove, formed by the laminate expansion of the 
front edge of the propleura (Fig. 1B, ppf), becomes so 
constricted between the procoxae that the corresponding 
segment of the rostrum is notably narrowed in order to fit 
into the narrow sinus. 


I am unaware of any illustration of the forewing for 
this species and provide a sketch (Fig. 1C) that shows the 
reduced venation and distribution of color. The striking 
white costal region is not mentioned in descriptions 
available to me, and in fact is invisible when the wings 
are withdrawn beneath the scutellum. 

As in related scutellerid genera, Camirus has 
subquadrate paramedian stridulatory areas on ventral 
segments 4 and 5, but they are almost invisible unless the 
specimen is turned into the correct inclination vis-d-vis a 
light source, when they are seen to consist of prominent 
long parallel striae. I could detect no corresponding 
plectral surfaces on the inner side of the metafemora aside 
from a few random subapical vertical striae which do not 
seem correctly placed to rub against the stridulatral 
surface. 


FAMILY PENTATOMIDAE 
Subfamily Pentatominae 


Proxys punctulatus (Palisot de Beauvois) 


At the time of preparing my 1971 treatment, I had seen 
material of this striking black and yellow species only 
from a few specimens taken in the cities of Richmond, 
Suffolk, Chesapeake, and Norfolk. From these localities 
I concluded the species observed the classical “Lower 


Fig. 1. Camirus porosus. 


A. Outline of body in dorsal aspect; B. Anterolateral aspect of forebody, showing 


deep insertion of the head into the prothorax and concealment of antennal socket under propleural flange (ppf); 
C. Left forewing. Heavily stippled area is dull black, lightly stippled area is ivory-white, unstippled areas are clear 
membrane, the veins are indicated somewhat more evidently than in actuality. 


14 BANISTERIA 


No. 19, 2002 


Fig. 2. Distribution of Proxys punctulatus in Virginia. Previously published records indicated by the plus symbols, new 
records by dots. Dashed line approximates the eastern edge of the Fall Line; solid line the eastern edge of the Blue 


Ridge. 


Austral” distribution and was probably confined to the 
Coastal Plain in Virginia. Material subsequently acquired 
by VMNH demonstrates a distinctly greater range: 
essentially everywhere east of the Blue Ridge. New 
localities are in Essex, Greene, Greensville, Halifax, 
Henry, Isle of Wight, Nelson, Nottoway, and Roanoke 
counties and justify preparation of a new state range map 
(Fig. 2) for this species. 

The westernmost capture sites correspond closely to a 
line drawn along the base of the Blue Ridge: Greene Co.: 
Conway River at Va. 230, 23 August 1980, RLH (1). 
Nelson Co.: Afton, 21 July 1973, J. Gainer (1). Roanoke 
Co.: Roanoke River at crossing of Blue Ridge Parkway, 
29 June 1975, S. W. Bullington (1). 

Although the species is attracted to UV light, 
specimens appear singly or in very small numbers, e.g., 
two from Greensville County on 15 July 1994. We have 
three specimens from Essex County taken in extensive 
Malaise trapping over a period of several seasons, an 
extremely low return considering the total trap effort of 
hundreds of hours. 


Subfamily Asopinae 


My 1971 treatment of Virginia pentatomoids did not 
admit this taxon at either the tribal or subfamilial level 
despite its treatment as a subfamily by Blatchley (1926) 
and other authorities. I herewith atone for that neglect by 
recognizing the Asopinae in the sense of Thomas (1992), 
who revised the asopine fauna of the Western Hemisphere 


and introduced a considerable number of nomenclatorial 
changes which I now review in order to update the names 
used in my 1971 accounts. 

Blatchley (1926: 93) distinguished the Asopinae from 
nominate Pentatominae by structure of the bucculae, long 
and parallel in the latter, almost entirely enveloping the 
slender basal segment of the rostrum, against short and 
convergent, enclosing only the basal half of the short, 
thick basal rostral segment in asopines. Thomas (1992: 
8) was unable to define tribal groups among the 27 New 
World genera that he recognized despite a diversity of 
structural features. Five of these genera are represented in 
the Virginia fauna and can be distinguished as follows: 


KEY TO THE VIRGINIA 
GENERA OF ASOPINAE 


1. Scutellum broad and ovoid, covering inner angles of 
hemelytral coria and base of membrane, the apex 


broadly rounded.....................0.0.000. 00. Stiretrus 
— Scutellum subtriangular. distally acuminate, not 
Covering Hemelyiracn....4.heuBein oh aes ia eek ih 2 


2. Rostrum very long, extending back to 2™ abdominal 
segment; pronotal humeri produced into blunt 
digitiform projection; color bluish-black with 
pronotum and scutellum variously ornamented 
with red markings....................... Euthyrhynchus 

— Rostrum shorter, not extending beyond posterior 
coxae; humeri, if produced, acute or spinose; 
color not dark blue and red.........................2.. 3 


HOFFMAN: STINK BUGS 15 


3. 4" segment of rostrum about twice as long as 3"; 


color black and orange......................... Perillus 
— 4" segment of rostrum about equal to 3"; color 
yellowish to brownish..................0 00000000 eee 4 
4. Jugae slightly longer than tylus; body length greater 
BUF. 50 Ta OA 10 Net Oe FO <n ON Ue A Ae Apoecilus 
— Jugae and tylus equal in length; body less than 
(Demin JONG... bss sinds onesie dhax. descivenni py OGISHS 


Euthyrhynchus floridanus (Linnaeus) 


In 1971 I cited material from Appomattox, 
Gloucester, and Southampton counties, and the cities of 
Suffolk, Norfolk, and Newport News. Specimens at 
VMNH add Isle of Wight County and the cities of 
Hampton, Richmond, and Virginia Beach. A specimen 
from Kiptopeke State Park, at the southern end of 
Northampton County (S.M. Roble, 6 October 1996) 
establishes the species on the “Eastern Shore” and one 
from Grey’s Point, Middlesex County (J. Carnes, 29 
October 1955) extends the Virginia range slightly 
northward to the Rappahannock River. 


Apoecilus cynicus (Say) 


Thomas (1992: 25) elevated Apoecilus from 
subgeneric to generic rank, in the process incidentally 
removing the generic name Apateticus from the local 
fauna. As Apateticus cynicus I reported this large and 
conspicuous species from Burkes Garden, Tazewell 
County, its only then-known Virginia locality. 

Recently collected VMNH specimens now represent 
the counties of Alleghany, Augusta, Bath, Bedford, Craig, 
and Dickenson, from sites on or west of the Blue Ridge. 
Robert Vigneault obtained eight specimens, mostly at 
lights, at Breaks Interstate Park, Dickenson County, 
during the first two weeks of July 2000. 


Podisus brevispinus Thomas 


The specific name modestus, by which this insect was 
known for many decades, was determined by Thomas 
(1992: 93) to have been based upon a specimen of P. 
maculiventris (Say), thus requiring the proposal of the 
new name brevispinus for the present species. As Podisus 
modestus 1 recorded it (1971: 58) from only a few 
specimens captured in Montgomery and Grayson 
counties. Recently acquired material originated in 
Augusta, Bath, Botetourt, Dickenson, Floyd, Giles, 
Highland, Nelson, Rockingham, Smyth, Tazewell, and 
Washington counties, from sites on or west of the Blue 
Ridge and nearly all above 3000 ft. elevation. 


Podisus placidus Uhler 
New state record, new southernmost locality 


A boreal species stated by Blatchley to have been 
“. not recorded south of New Jersey.” Localities cited 
by Froeschner (1988: 556) define a range from Quebec to 
Alberta and Utah, again with nothing south of New Jersey 
and Ohio. VMNH has a single female collected by 
Malaise trap in Clarke Co.: Blandy Experimental Farm, 3 
mi. S Boyce (D. R. Smith, 2 July 1991), which adds the 
species to to the state list of insects, and constitutes a 
considerable southward extension of the known range. 
Whether this specimen derived from a native population, 
or was introduced via shrubbery (Blandy Farm hosts a 
variety of exotic cultivars) remains to be determined by 
future collections in Virginia and neighboring states. 
The combination of straight pronotal margins, 
immaculate legs and membrane, and extensive random 
brown blotching of the dorsum readily distinguish this 
species from other local members of the genus. 


Podisus neglectus (Westwood) 


Based on a single female without indication of origin, 
this species fell into an obscurity that was a credit to its 
name. The type specimen was apparently not restudied by 
a pentatomid specialist until Thomas found it in the 
British Museum collection and recognized the species as 
that described much later as P. fretus (Olsen, 1916) from 
specimens taken in Massachusetts. Ranging from Maine 
to Florida along the seacoast, with disjunct populations in 
the Great Lakes region; the species appears to be 
uncommon in Virginia as no specimens have been taken 
here since I reported two specimens (USNM) from 
Virginia Beach. Since there has been no dearth of 
collecting activities in the two “Eastern Shore” counties 
and extreme southeastern Virginia by staff of the Division 
of Natural Heritage, perhaps some special collecting 
techniques are required to obtain specimens of P. 
neglectus. That an actual hiatus in the range may occur, 
however, is suggested by the apparently analogous case of 
another coastal pentatomid, Thyanta custator (Fabricius), 
of which no specimens have been taken between New 
Jersey and North Carolina. 


Podisus serieventris Uhler 


Known states of record for this species clearly reflect 
a northern, subboreal distribution from Newfoundland to 
British Columbia, and southward to North Carolina and 
Utah. Curiously, the only Virginia records I could cite in 
1971 were for Arlington and Fairfax counties, in the 
Piedmont rather than the mountains, an anomaly 
paralleled by the localities then known for North Carolina. 


16 BANISTERIA 


Since 1971, a few captures have been made in the 
Virginia mountains: Dickenson Co.: Breaks Interstate 
Park, 1-14 July 2000, Robert Vigneault (6), and Highland 
Co.: Locust Spring Recreation Area, George Washington 
National Forest, 29 April 1972, R. L. and L. S. Hoffman 
(1). Collectively, these do not add up to a very adequate 
picture of the in-state distribution. 

The addition of P. placidus to the state fauna and the 
several name changes mentioned above require revision 
of the key that I prepared in 1971. 


KEY TO THE VIRGINIA 
SPECIES OF PODISUS 


1. Dorsolateral margin of pronotum straight; legs 
and membrane immaculate; dorsum mostly 
pale beige mottled with irregular brown 
IDLOTCHES Sh mata swgthi a: Rabon Memiel tune hone P. placidus 
— Dorsolateral margin of pronotum concave or 
indented near midlength; membrane with 
median stripe; dorsum colored otherwise............2 
2. Legs immaculate yellow; median projection of 
2™ ventral segment short, not extending 
between metacoxae; body length less than 
OPTAIN es chek oPeats We nae eel a ae P. brevispinus 
— Legs variously marked with spots or annulations; 
median projection of 2" ventral segment longer, 
usually extending between bases of metacoxae; 
length greater than 10 mm..................... 0.00.02. 3 
3. Femora of all legs with two black subapical spots 
Be a a cn wre ie ete se ae P. maculiventris 
— Femora variously marked but never with two 
subapiCal dark: Spots. ins ccoics ceuxleateigs pense ey ese 4 
4. Antennae uniformly light reddish-brown; 
midventral abdominal spots large (size of an 
eye, or larger) and poorly-defined........P. neglectus 
— 3™ and 4" antennomeres distinctly darker than basal; 
midventral abdominal spots small and sharply 
GETING. Wena et AL Pe a nae P. serieventris 


SUMMARY 
The 84 species of Pentatomoidea now known to 


occur in Virginia are distributed among four families as 
follows: 


No. 19, 2002 
Scutelleridae 8 
Cydnidae 14 
Corimelaenidae 11 
Pentatomidae 51 


The proximity of capture sites for other species in 
adjoining states suggests that this total may increase to 
about 90 through continued collecting efforts. 


LITERATURE CITED 


Blatchley, W. S. 1926. Heteroptera or True Bugs of 
Eastern North America, with Especial Reference to the 
Faunas of Indiana and Florida. Nature Publishing Co., 
Indianapolis. 1116 pp. 


Froeschner, R.C. 1988. Families Pentatomidae (pp. 544- 
597) and Scutelleridae (pp. 684-693) In T. J. Henry & 
R. C. Froeschner. Catalog of the Heteroptera, or True 
Bugs, of Canada and the Continental United States. 
E. J. Brill, Leiden and New York. 958 pp. 


Hoffman, R. L. 1971. Shield bugs (Hemiptera: 
Scutelleroidea: Scutelleridae, Corimelaenidae, Cydnidae, 
Pentatomidae). The Insects of Virginia, No. 4. Research 
Division Bulletin 67, Virginia Polytechnic Institute and 
State University, Blacksburg. 61 pp. 


Hoffman, R. L. 1994. Additions and corrections to the 
Virginia fauna of “True Bugs” (Heteroptera: Cydnidae, 
Scutelleridae, Pentatomidae, Alydidae). Banisteria 3: 15- 
19. 


Jones, M. P. 1935. A peculiar insect situation along a 
seashore. Proceedings of the Entomological Society of 
Washington 37: 150-151. 


Olsen, C. E. 1916. A new pentatomid. Bulletin of the 
Brooklyn Entomological Society 11: 82-83. 


Thomas, D. B. 1992. Taxonomic synopsis of the asopine 
Pentatomidae (Heteroptera) of the Western Hemisphere. 
Thomas Say Foundation Monographs 16: 1-156. 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


Second Update to the Survey of Macrolepidopteran Moths 
Near Vontay, Hanover County, Virginia 


J. Christopher Ludwig 


Virginia Department of Conservation and Recreation 
Division of Natural Heritage 
217 Governor Street 
Richmond, Virginia 23219 


INTRODUCTION 


This paper provides a second update to the list of 
macrolepidopteran moth (= “macro-moth” or “macro” 
species collected at a site on the Virginia Piedmont, 
2 km W of Vontay in western Hanover County. 
A description of the study site, methodology, and 
original species list were given in Ludwig (2000) and 
the first update was provided in Ludwig (2001). The 
new collections extend the study to five years (30 
October 1996 to 30 October 2001) and increase the 
number of collection nights to >470. The species list 
from this study, along with others being gathered 
throughout Virginia by the Virginia Department of 
Conservation and Recreation’s Division of Natural 
Heritage, is being used to ascertain the biological status 
and develop a complete list of the Commonwealth’s 
macro-lepidopteran moths. 


RESULTS AND DISCUSSION 


A total of 82 macroleptidopteran moth specimens 
was pinned and identified during the extended study 
period, bringing the total number of collected 
specimens at this site to 2,170. These collections 
increased the number of species documented at this site 
from 521 to 530 and the number of genera from 298 to 
300 (Table 1 and Appendix). The Noctuidae (310 
species) and Geometridae (103) were most diverse with 
the Arctiidae (34) and Notodontidae (33) also rich. 

An updated species-accumulation curve (Fig. 1) for 
this study indicates that additional macros will be 
recorded at the site should collections continue. 
Depending upon the projected trajectory of the curve, 
estimates of the total number of taxa recorded from this 
site over 10 years range from 570-680 macro-moth 
species, representing perhaps as much as 50% of the 
state’s estimated total macro fauna. 


Noted as absent from the site’s original collections 
(Ludwig, 2000), two Eurasian moth species have now 
been recorded at the study site. A single Noctua 
pronuba L. was found on 29 May 2000 (Ludwig, 
2001), reinforcing its status as a widespread, recent 
introduction to Virginia (Roble et al., 1999). A male 
gypsy moth, Lymantria dispar L., was found on 3 July 
2001, presumably representing the first of many to 
inhabit the site as the line of infestation moves south 
and east from the northwestern Virginia Piedmont. 


Table 1. Summary of macro-moths encountered during 
this study by family given in order of Hodges et al. 
(1983). 


Family Genera Species Specimens 
Thyatiridae 2 2 9 
Drepanidae 3 eB Ke 
Geometridae 69 103 394 
Epiplemidae 2 2 5 
Mimallonidae 1 1 6 
Apatelodidae 2 2 4 
Lasiocampidae 4 i) 8 
Saturniidae 10 Li 12 
Sphingidae 12 18° 33 
Notodontidae 18 a8 138 
Arctiidae 18 34 94 
Lymantriidae ) 6 26 
Noctuidae 158 310 1434 
TOTALS 300 530 2170 


“ Four species documented by sight records only 


> One species documented by sight record only 


18 BANISTERIA 


ACKNOWLEDGMENTS 


Rebecca Wilson assisted with fieldwork. 
Manuscript preparation was funded in part by the 
Virginia Department of Conservation and Recreation, 
Division of Natural Heritage. All specimens are 
currently housed in the DNH reference collection. 


LITERATURE CITED 


Covell, C. V., Jr. 1999. The Butterflies and Moths 
(Lepidoptera) of Kentucky: An Annotated Checklist. 
Kentucky State Nature Preserves Commission, 
Scientific and Technical Series 6. 220 pp. 


Hodges, R. W., T. Dominick, D. R. Davis, D. C. 
Ferguson, J. G. Franclemont, E. G. Munroe, & J. A. 
Powell. 1983. Check List of the Lepidoptera of 
America North of Mexico. E.W. Classey Ltd. & The 


No. 19, 2002 
Wedge Entomological Foundation, London. 284 pp. 


Ludwig, J. C. 2000. A survey of macrolepidopteran 
moths near Vontay, Hanover County, Virginia. 
Banisteria 15: 16-35. 


Ludwig, J. C. 2001. An update to the survey of 
macrolepidopteran moths near Vontay, Hanover 
County, Virginia. Banisteria 17: 42-47. 


Rings, R.W., E.H. Metzler, F.J. Arnold, & D.H. Harris. 
1992. The Owlet Moths of Ohio Order Lepidoptera 
Family Noctuidae. Ohio Biological Survey Bulletin. 
New Series 9 (2). 219 pp. 


Roble, S. M., A. C. Chazal, C. S. Hobson, & J. C. 
Ludwig. 1999. First records of Noctua pronuba L., an 
Old World moth, in Virginia (Lepidoptera: Noctuidae). 
Banisteria 14: 45-47. 


Appendix. Additional macro-moth species identified during this study given in order of Hodges et al. (1983). 
Fields are: checklist number, species name, collection date (month/day/year), method (s=sugar bait, b=black light, 
i=incandescent light, m=mercury vapor light); numbers in parentheses indicate if number of specimens is > 1 for a 
given date and survey method. Asterisks denote species new for the study. 


Drepanidae 
6251 Drepana arcuata (W1k.) 04/06/01 m 
Geometridae 
6258 Alsophila pometaria (Harr.) 02/20/01 1 
*6405 Semiothisa gnophosaria (Gn.) 05/25/01 m 
6586 Anacamptodes defectaria (Gn.) 04/17/01 m 
6662 Paleacrita vernata (Peck) 02/20/01 i 
6843 Plagodis fervidaria (H.-S.) 07/08/01 m 
6885 Besma quercivoraria (Gn.) 05/02/01 m 


6894.x Lambdina athasaria (W1k.) complex 


04/17/01 m 
7033 Nemoria lixaria (Gn.) 09/25/01 m 
7132 Pleuroprucha insularia (Gn.) 09/25/01 i 
7196 Eulithis diversilineata (Hbn.) 07/14/01 m 
7292 Hydria prunivorata (Fgn.) 06/12/01 m 
*7638 Cladara angulineata (Grt.&Rob.) 04/06/01 m 
Saturniidae 
7765 Callosamia angulifera (W1k.) 06/16/01 m, 
07/13/01 m 


Sphingidae 
*7786 Ceratomia amyntor (Geyer) 07/28/01 m 
Notodontidae 
*7896 Clostera inclusa (Hbn.) 04/06/01 m 
7931 Gluphisia septentrionalis (W1k.) 05/15/01 m 
7999 Lochmaeus bilineata (Pack.) 08/13/01 m 
Arctiidae 
8104 Comachara cadburyi Franc. 05/02/01 m 
Lymantriidae 
8314 Orgyia definita Pack. 07/06/01 m, 
07/28/01 m, 10/06/01 m (2) 
*8318 Lymantria dispar (L.) 07/03/01 m 


Noctuidae 


8338 Phalaenophana pyramusalis (W1k.) 05/25/01 m 
8426 Dyspyralis illocata Warr. 06/11/01 m 


LUDWIG: VONTAY MOTHS 19 


Noctuidae (continued) 


8499 
8505 
8525 
8692 
*8703 
8792 
8849 
8898 
8904 
8907 
8959 
8962 
9037 
9038 


9040 
9051 


9062 
9169 
O27 1 
9243 
9244 
9251 
O22 


Metalectra discalis (Gtt.) 09/10/01 m 
Metalectra richardsi Brower 07/12/01 m 
Phyprosopus callitrichoides Grt. — 07/24/01 m 
Zale galbanata (Mortrr.) 07/24/01 m 
Zale duplicata (Bethune) 04/03/01 m 
Catolcala vidua (J.E. Sm.) 09/25/01 m 
Catocala andromedae Gn. 07/06/01 m 
Allagrapha aerea (Hbn.) 07/28/01 m 
Chrysanympha formosa (Gtt.) 06/11/01 m 
Megalographa biloba (Steph.) 05/15/01 m 
Paectes pygmaea (Hbn.) 08/13/01 m 
Paectes abrostoloides (Gn.) 10/16/01 1 


Hyperstrotia pervetens (B.&McD.) 06/05/01 m 
Hyperstrotia villificans (B.&McD.) 
05/15/01 m (2) 
Hyperstrotia secta (Gtt.) 05/15/01 m 
Lithacodia musta (Grt.&Rob.) 06/05/01 m, 
08/13/01 m 
Cerma cerintha (Tr.) 06/10/01 m 
Bagisara rectifascia (Gtt.) 07/04/01 m 


Acronicta funeralis (Grt. & Rob.) 06/12/01 m 
Acronicta ovata Gtt. 07/28/01 m 
Acronicta modica Wk. 05/15/01 m 
Acronicta retardata (W1k.) 05/02/01 m 
Acronicta oblanita (J.E. Sm.) 06/10/01 m 


9427 Meropleon diversicolor (Morr.) — 09/25/01 m 
9466 Papaipema cataphracta (Gtt.) 10/03/01 1, 
10/16/01 i, 10/20/01 i 
9485 Papaipema baptisiae (Bird) 09/18/00 m 
9501 Papaipema eupatorii (Lyman) 10/03/01 1 
9556 Chytonix palliatricula (Gn.) 05/25/01 m 
9688 Galgula partita Gn. 07/01/01 m, 
07/04/01 m (2), 07/06/01 m, 07/14/01 m 

9892 Lithophane disposita Morr. 10/20/01 1 
9961 Anathix ralla (Grt. & Rob.) 09/10/01 m 
10021 Copivaleria grotei (Morr.) 04/06/01 m 
10304 Trichordestra legitima Gtt. 09/01/01 m 
10368 Lacinipolia meditata (Gtt.) 09/20/01 m 
10397 Lacinipolia renigera (Steph.) 09/20/01 m 
10501 Crocigrapha normani (Gtt.) 04/17/01 m 
10502 Himella intractata (Morr.) 04/12/01 m 
10518 Achatia distincta Hbn. 04/12/01 m, 
05/02/01 m 
10521.1 Morrisonia latex (Gn.) 05/02/01 m 
10648 Agrotis gladaria Morr. 10/06/01 m 
10915 Peridroma saucia (Hbn.) 04/14/01 m 
10944 Xestia smithii (Snell.) 09/24/01 m 
10998 Choephora fungorum Grt. & Rob. 10/03/01 i 
11006 Protolampra brunneicollis (Grt.) 09/25/01 m 


11128 
11135 


09/20/01 m 
08/20/01 m 


Schinia arcigera (Gn.) 
Schinia rivulosa (Gn.) 


Figure 1. Species accumulation curve for macrolepidopteran moths encountered during this study. 


om 
[<b] 
= x 
sf 
os 
2s 
<6 
so 
E 
(o) 
S) 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


Status of the Rare Skipper (Problema bulenta) in Virginia 


Anne C. Chazal and Christopher S. Hobson 


Virginia Department of Conservation and Recreation 
Division of Natural Heritage 
217 Governor Street 
Richmond, Virginia 23219 


The life history of the rare skipper (Problema 
bulenta) is poorly documented. It is associated with 
tidal marshes or upland habitats with abundant nectar 
sources in the vicinity of tidal marshes. Larvae are 
suspected to feed on giant cordgrass (Spartina 
cynosuroides), southern wild rice (Zizaniopsis 
miliacea), and wild rice (Zizania aquatica) (Opler & 
Krizek, 1984; Cromartie & Schweitzer, 1993; 
Glassberg, 1999). Recently, late instar larvae were 
found on Phragmites australis in New Jersey (D. F. 
Schweitzer, pers. comm.). Despite the widespread 
occurrence of apparently suitable habitat, the rare 
skipper tends to be highly localized and sporadic in 
distribution. 

The rare skipper has been documented from seven 
states along the Atlantic coast: New Jersey, Delaware, 
Maryland, Virginia, North Carolina, South Carolina, 
and Georgia (Cromartie & Schweitzer, 1993; Opler, 
1998). The rare skipper was formerly a candidate 
(Category 2) species for listing under the federal 
Endangered Species Act, until the U.S. Fish and 
Wildlife Service abolished that category in 1996. 
Currently, it receives no legal protection in any of the 
states in which it occurs, despite its rarity and patchy 
distribution. 

The rare skipper has one brood from late-July to 
August in the northern portion of its range (Opler & 
Krizek, 1984). There are records from May and early 
June indicating it 1s double-brooded in the southern 
portion of its range (Opler & Krizek, 1984). In Virginia, 
Nicolay (1979) proposed that the rare skipper might be 
double-brooded, while Opler & Krizek (1984) 
suggested that it is single-brooded. All of the Virginia 
collections to date are from late-July and August; 
however, extensive survey efforts have not been 
conducted earlier in the year. 

In Virginia, J. Bauer and B. Dixon first collected P. 
bulenta on 21 August 1967 (Covell & Straley, 1973). 
The location was reported as 2.0 miles (3.2 km) south 
of Lanexa, New Kent County. The area consists of 


tidal marshes along the Chickahominy River near its 
confluence with Diascund Creek (Nicolay, 1979; 
Pague, 1991; Hobson, pers. obs.). R. Anderson, S. 
Nicolay, C. Covell, and G. Straley collected P. bulenta 
from the flowers of swamp milkweed  (Asclepias 
incarnata) at this location in August 1970 (Covell & 
Straley, 1973). Anderson and Nicolay captured it again 
in August of 1971, but efforts by Anderson in mid-July 
1971 were unsuccessful (Covell & Straley, 1973). 

C. S. Hobson and S. M. Roble reverified this 
population on 23 August 1999, when they observed 
nine adults at two marshes upstream of the mouth of 
Diascund Creek. Eight of the individuals were seen 
nectaring on pickerelweed (Pontederia cordata) about 
1-1.75 km upstream of the mouth of Diascund Creek in 
New Kent County. One individual was on swamp 
milkweed approximately 6 river km upstream of the 
mouth of Diascund Creek, Charles City County (new 
county record). A survey conducted at these sites on 31 
August 1999 did not find any P. bulenta, however 
weather conditions were less than favorable. 

Associated butterflies and skippers at these capture 
sites included broad-winged skipper (Poanes viator), 
orange sulphur (Colias eurytheme), palamedes 
swallowtail (Papilio palamedes), red admiral (Vanessa 
atalanta), fiery skipper (Hylephila phyleus), spicebush 
swallowtail (Papilio troilus), tiger swallowtail (Papilio 
glaucus), and monarch (Danaus plexippus). 

Vegetation at the capture sites 1s characterized by 
dense stands of southern wild rice mixed with wild rice, 
pickerelweed, arrow arum (Peltandra virginica), and 
two species of mallows (Hibiscus moscheutos, 
Kosteletzkya virginica). Giant cordgrass was not 
observed in the vicinity of the captures, but was found 
in small patches within three miles downstream of 
Diascund Creek. Bald cypress (Taxodium distichum) is 
prevalent along the floodplain in the vicinity of the 
capture sites. 

Additional surveys of other tidal marshes in 
Virginia in 1999 failed to document the presence of 


CHAZAL & HOBSON: RARE SKIPPER 21 


P. bulenta. These included surveys along the 
Rappahannock, Mattaponi, and Pamunkey rivers. 
Extensive surveys of marshes along the Rappahannock 
River were also conducted in July and August of 2001 
without success. 

While conducting zoological surveys in 2001 for the 
National Park Service at Colonial National Historical 
Park — Jamestown Island, P. bulenta was observed by 
Chazal and others at one small, fringe marsh over the 
course of several weeks. The marsh is approximately 
50 m long by 20 m wide and is approximately 0.8 mi 
(1.25 km) north of Travis Cemetery on Jamestown 
Island, in James City County, Virginia (new county 
record). The area within which P. bulenta was observed 
covers approximately 6.4 acres (2.6 ha). This is only 
the second known Virginia population of this species 
and is approximately 24 air km south of the previously 
known site on the Chickahominy River. 

Emergent vegetation in this area includes giant 
cordgrass, arrow arum, narrow-leaved cattail (7ypha 
angustifolia), and pickerelweed. Larger, surrounding 
marshes contain giant cordgrass, arrow-arum, wild rice, 
dotted smartweed (Polygonum punctatum), halberd-leaf 
tearthumb (Polygonum arifolium), Walter’s barnyard 
grass (Echinochloa waliteri), bull-tongue arrowhead 
(Sagittaria lancifolia), and other species. Several stems 
of swamp milkweed were observed along the edge of 
the marsh on the upland side. 

On 19 July 2001, one P. bulenta was collected; 
however, it was not identified until about one month 
later and its precise capture location is uncertain. Based 
on surveys in the area after this finding, and the highly 
localized behavior of the species, the collection was 
almost certainly made in the same fringe marsh as the 
subsequent observations and collections. On 15 August, 
8-9 individuals of P. bulenta were observed in the outer 
portions of the marsh. The highest population count 
occurred on 22 August when 139 individuals were 
observed near the Colonial Parkway. A majority (106) 
of those seen on this date were observed nectaring on 
20-30 flower heads of swamp milkweed (Fig. 1). On 
30 August, only ten P. bulenta were observed. It was 
also noted that the swamp milkweed flower heads were 
either spent, or appeared to have been browsed by 
white-tailed deer (Odocoileus  virginianus). Rare 
skippers were last observed on 6 September when four 
individuals were seen. None were seen on 13 
September. 

The rare skippers were observed nectaring mainly 
on swamp milkweed and_ pickerelweed’ with 
two individuals observed nectaring on rattlesnake 
master (Eryngium aquaticum). Outside of Virginia, 
other reported nectar sources of P. bulenta include 


buttonbush (Cephalanthus occidentalis), common 
milkweed (Asclepias syriaca), dogbane (Apocynum 
cannabinum), swamp rose mallow (Hibiscus palustris), 
and seashore mallow (Kosteletzkya virginica) (Krizek 
& Opler, 1986; Cromartie & Schweitzer, 1993). The 
latter authors listed numerous additional, infrequently 
visited plants. 

Other lepidopterans observed in the same area of 
Jamestown Island included broad-winged skipper, 
sedge skipper (Euphyes dion), Delaware skipper 
(Anatrytone logan), silver-spotted skipper (Epargyreus 
clarus), and monarch. 


Fig, 1. 
swamp milkweed (Asclepias incarnata). 


Adult rare skipper (Problema bulenta) on 


ACKNOWLEDGMENTS 


Many people assisted with fieldwork during the 
surveys conducted at Colonial National Historical Park, 
including Joe Weber, Gina Pisoni, Kathy Derge, and 
Lisa Page Carter. Funding for the surveys was provided 
by the United States Department of the Interior, 
National Park Service, through cooperative agreement 
number 4000-8-9027 number 2 with the Virginia 
Department of Conservation and Recreation, Division 
of Natural Heritage. The Virginia Department of 
Agriculture and Consumer Services in cooperation with 
the U. S. Fish and Wildlife Service provided funding to 
the Virginia Department of Conservation and 
Recreation, Division of Natural Heritage for the 
fieldwork conducted in 1999. Steve Roble, Amber 
Foster, Dean Walton, and Phil Coulling provided field 
assistance. 


22 BANISTERIA 


LITERATURE CITED 


Covell, C. V., Jr., & G. B. Straley. 1973. Notes on 
Virginia butterflies with two new state records. Journal 
of the Lepidopterists’ Society 27: 144-154. 


Cromartie, W. J., & D. F. Schweitzer. 1993. Biology of 
the rare skipper (Hesperiidae), in southern New Jersey. 
Journal of the Lepidopterists’ Society 47: 125-133. 


Glassberg, J. 1999. Butterflies Through Binoculars — 
The East: A Field Guide to the Butterflies of Eastern 
North America. Oxford University Press, New York, 
NY. 242 pp. 


Krizek, G. O., & P. A. Opler. 1986 [1987]. 
Observations on Problema bulenta. Journal of Research 
on the Lepidoptera 25: 146-148. 


No. 19, 2002 


Nicolay, S. S. 1979. Problema bulenta (Boisduval and 
LeConte). Pp. 173-174 In D. W. Linzey (ed.). 
Endangered and Threatened Plants and Animals of 
Virginia. Virginia Polytechnic Institute and State 
University, Blacksburg, VA. 


Opler, P. A. 1998. A Field Guide to Eastern 
Butterflies. Houghton Mifflin Company, Boston, MA. 
486 pp. 


Opler, P. A., & G. O. Krizek. 1984. Butterflies East of 
the Great Plains. The Johns Hopkins University Press, 
Baltimore, MD. 294 pp. 


Pague, C. A. 1991. Rare skipper Problema bulenta 


(Boisduval and LeConte). Pp. 238-240 Jn K. 
Terwilliger (coordinator). Virginia’s Endangered 
Species. McDonald and Woodward Publishing 


Company, Blacksburg, VA. 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


First Virginia Records for Three Species of Centipeds 
(Geophilomorpha: Schendylidae) 


Richard L. Hoffman 


Virginia Museum of Natural History 
Martinsville, Virginia 24112 


Luis A. Pereira 


Museo de La Plata 
RA 1900 
La Plata, Argentina 


The recent annotated list of Virginia centipeds 
(Hoffman, 1995) admitted 56 species confirmed for the 
state as well as 19 others considered as likely to be found 
here. Yet, despite ongoing collecting efforts in the past 
six years, disappointingly little augmentation of the 
original total has taken place. We take this occasion to 
put on record three species of the family Schendylidae 
new to Virginia, two of them more or less anticipated, the 
third so far out of its known range as to be of particular 
biogeographic interest. 

With these additions, Virginia is known to harbor no 
fewer than six species of schendylids, the greatest number 
recorded for any state, and hardly equalled by any area of 
comparable size in the world. Yet it is entirely probable 
that additional endemic species remain to be discovered 
here. 


SCHENDYLIDAE 


The distribution of this family is curious. By far the 
great majority of both genera and species occur 
throughout the Neotropical, Indoaustralian, and 
Afrotropical regions, but another contingent is distinctly 
Holarctic and notably psychrophilus in terms of surface 
activity. The group itself was not established until 1896, 
when O. F. Cook dismembered the old Geophilidae into 
nine clearly-defined families. At that time, Cook knew 
only one endemic genus (Escaryus) and its two species in 
eastern North America, in addition to a European species 
introduced into New York state. 

Subsequently the Nearctic fauna was shown in many 
papers by R. V. Chamberlin to be large and diverse, with 
its greatest development in southwestern United States. 
The fauna of northeastern United States (two genera, four 


species) was treated by Crabill (1953), who later (1961) 
provided a catalog of the schendylids of North America, 
including Mexico (11 genera, 40 species, nearly all named 
by Chamberlin). Most recently, the present authors 
published a revision of the genus Escaryus, recognizing 
eight Nearctic species (Pereira & Hoffman, 1993). Since 
our native schendylids are normally found only during the 
colder months (or at high elevations in our latitude), they 
are not adequately represented in collections, and 
undoubtedly many major contributions to their knowledge 
remain to be made. This is shown clearly by our 
discovery in 1988 of two sympatric new species of 
Escaryus in the Virginia Blue Ridge, and by the three 
species of Schendylidae here added to the known fauna of 
the state. 


Schendyla nemorensis (C. L. Koch) 


This species is common in western Europe, and like 
so many other small soil animals has been introduced into 
a hospitable North America where it is now widely 
dispersed and abundant in urbanized areas of the northern 
states. Crabill (1953) mentioned localities in Connecticut, 
Illinois, Massachusetts, Michigan, New Hampshire, 
New York, and Utah, and predicted eventual discovery in 
many others. We now add Virginia, apparently the 
southernmost established state of record: 

Roanoke Co.: Salem, 1 February 2002, 2 Oo 
(VMNH). A sample of soil taken beneath a white pine in 
his backyard by Dr. Jorge Santiago-Blay and processed by 
Berlese extraction at VMNH yielded these specimens. 
The larger is 20 mm in length, with 39 pairs of legs; both 
agree in every respect with the detailed description and 
illustrations published by Brélemann & Ribaut (1912). 


24 BANISTERIA 


The species is easily recognized by the form of the 
terminal legs of males (Fig. 1). Males of Escaryus 
likewise have enlarged podomeres, but they are densely 
setose and the terminal article is not so strongly reduced 
and set off. S. nemorensis differs also in having only four 
coxopleural pores instead of 12 or more, and in that the 
terminal claw of the second maxillae is not pectinate. 
Both conditions can be seen without dissection from a 
specimen mounted in ethylene glycol or lactic acid. 


Fig. 1. Schendyla nemorensis, posterior end of body in 
ventral aspect, showing form of the last pair of legs with 
the reduced 7" podomere, and position of the four 
coxopleural pores beneath the last sternal plate, characters 
which distinguish this species from other local 
geophilomorphs. Specimen from Salem, Virginia. 


Escaryus liber Cook & Collins 


Originally described from New York state, this 
species remained largely unknown until Crabill’s 
treatment in 1953, when he added localities for Ohio, 
Maryland, and the District of Columbia. The last two 
places almost guaranteed discovery of E. liber in Virginia, 
and this had even happened some years before the work 
by Pereira & Hoffman (1993) appeared. Ironically, the 
specimen was at VMNH but unknown to them, in a 
backlog of unsorted samples. 

Rockbridge-Bedford Cos.: Blue Ridge Parkway, 0.5 
mi N Petite’s Gap, in pine-maple woods, 3 December 
1988, W.A. Shear (VMNH 19 adult, 25 mm long, with 
51 pairs of legs, both spermathecae contain mature 


No. 19, 2002 


spermatozoa). 

The species has not been recovered despite several 
attempts made at the specified site and higher on Apple 
Orchard Mountain. It has been described and illustrated 
in detail by Pereira & Hoffman (1993). 


Escaryus ethopus Chamberlin 


Heretofore this species has been recorded only from 
Alaska and Yukon Territory, Canada (Pereira & Hoffman, 
1993, Map 1). Although widely disjunct distributions 
between the Appalachians and western North America 
have long been known, they have been almost invariably 
at the generic level. The present case involves a 
separation of more than 2600 mi/4160 km and 
displacement far to the south from the subarctic primary 
area (Fig. 2). Fragmentation of a once continuous North 
American range may be invoked as the only plausible 
explanation; the existence of other small disjunct 
populations may be reasonably assumed. 


Fig. 2. Outline map of North America, showing primary 
range of Escaryus ethopus in Canada and Alaska 
(shaded), and location of site in the Virginia Blue Ridge 
(arrow). 


HOFFMAN & PEREIRA: CENTIPEDS 2 


Rockbridge-Bedford Cos.: Blue Ridge Parkway, 0.5 
mi N Petite’s Gap, in pine-maple woods, 3 December 
1988, W. A. Shear (VMNH 19 adult, 40 mm long, with 
49 pairs of legs, seminiferous tubules with mature 
spermatozoa). 

This specimen agrees with the detailed description of 
E. ethopus (Pereira & Hoffman, 1993: 52-56) in every 
respect except that the pretergum of the last pedal 
segment is separated from the pleurites by sutures. 
Whether this single difference is only an aberration or 
reflects a constant difference in the Virginia population 
cannot be ascertained until more material has been 
examined. Regrettably, despite numerous attempts to 
recollect this species at the specified locality and other 
sites in the central Blue Ridge, no additional specimens 
have been obtained. As with many minute soil animals, 
capture is often a matter of mere serendipity, and 
sampling efforts may miss a population by only a few 
meters. 


Escaryus urbicus (Meinert) 


This species has been recorded (Pereira & Hoffman, 
1993: 16) from western Virginia: Alleghany, Augusta, 
Bland, Giles, and Nelson counties. It is now possible to 
add an additional capture site: Floyd Co.: Buffalo 
Mountain Natural Area Preserve, north slope pitfall site 
at 3400 ft., December 2001-11 April 2002, (VMNH 1 GC, 
ca. 34 mm long, with 41 pairs of legs). This specimen 
agrees closely with the detailed description and 
illustrations presented by Pereira & Hoffman (1993; Figs. 
1-10), except that the labral teeth are much more distinct 
and darkly pigmented than shown in their Fig. 8, which 
may have been of an atypical condition. The appearance is 
much more like that represented for E. cryptorobius 
(Pereira & Hoffman, 1993; Fig. 55). 

Although the new locality is only slightly further 
south than that in Bland County, it establishes the species 
less than 30 miles from North Carolina and the discovery 
of E. urbicus in that state is virtually assured. Escaryus 
cryptorobius has been taken syntopically at Buffalo 


Mountain, although from Berlese extractions rather than 
pitfalls. 


ACKNOWLEDGMENTS 


We express our appreciation to Dr. Jorge Santiago- 
Blay and Prof. William A. Shear for generously donating 
material upon which this report is based to the Virginia 
Museum of Natural History. 


LITERATURE CITED 


Brolemann, H. W., & H. Ribaut. 1912. Essai d’une 
Monographie des Schendylina (Myriapodes, Géophilo- 
morphes). Nouvelles Archives du Muséum d’Histoire 
Naturelle, Mémoires, cinquiéme série 4: 53-183. 


Cook, O. F. 1896. An arrangement of the Geophilidae, a 
family of Chilopoda. Proceedings of the United States 
National Museum 18: 63-75. 


Cook, O. F., & G. N. Collins. 1891. Notes on North 
American Myriapoda of the family Geophilidae, with 
descriptions of three genera. Proceedings of the United 
States National Museum 13: 383-396. 


Crabill, R. E. 1953. The Schendylidae of northeastern 
North America (Chilopoda: Geophilomorpha). Journal of 
the New York Entomological Society 61: 93-98. 


Crabill, R. E. 1961. A catalogue of the Schendylinae 
of North America including Mexico, with a generic key 
and proposal of a new Simoporus (Chilopoda: 
Geophilomorpha). Entomological News 72: 29-36, 67-80. 


Hoffman, R. L. 1995. The centipeds (Chilopoda) of 
Virginia: a first list. Banisteria 5: 20-32. 


Pereira, L. A., & R. L. Hoffman. 1993. The American 
species of Escaryus, a genus of Holarctic centipeds 
(Geophilomorpha: Schendylidae). Jeffersoniana 3: 1-72. 


26 BANISTERIA 


No. 19, 2002 


SHORTER CONTRIBUTIONS 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


SPRING DRAGONFLY (ODONATA) AND 
BUTTERFLY (LEPIDOPTERA) FALLOUT AT THE 
CHESAPEAKE BAY  BRIDGE-TUNNEL.--Large 
groups of migrating Odonata are rare, especially in 
spring (Russell et al., 1998). On 27 May 2000, from 
about 1530 h to 1630 h, I encountered a fallout, or mass 
grounding, of dragonflies, butterflies, and other insects 
on the Chesapeake Bay Bridge-tunnel, at the mouth of 
Chesapeake Bay. The “other” insects were mostly 
beetles and were not studied. A thunderstorm was 
rapidly approaching, that soon produced heavy rain, 
causing me to leave after making observations on the 
three northernmost of four total man-made islands. The 
temperature was about 32° C and humidity was near 
100%. Winds were moderate from the east and had 
been strong, from the east, off the ocean, for the 
previous two days. 

I am a volunteer bird and butterfly researcher for 
Coastal Virginia Wildlife Observatory and while the 
Observatory has conducted regular butterfly surveys at 
the tip of Virginia’s Eastern Shore since 1995, 
dragonfly study has been very limited. The bridge- 
tunnel is a well-known migrant bird trap at all seasons 
(Kain & Brinkley, 1997) and I have crossed it regularly 
throughout the year for more than 25 years and have not 
witnessed a similar insect fallout there. 

I am not a dragonfly expert, but I am familiar with 
many species. I made sketches and notes of the 
dragonflies that were perched on the building walls and 
could be examined closely. I later made my 
identifications using Dunkle (2000) and the dragonfly 
website at http://members.bellatlantic.net/~dbarber/ 
odonatology.html. I counted more than 500 dragonflies 
on the 10 m by 10 m brick south wall of the building on 
the next to southernmost island. Many appeared to be 
escaping the strong wind by resting on the walls, but 
others were flying or were perched on vegetation out in 
the open. I estimated a total of 4,500 dragonflies over a 
distance of about 13 km along the bridge-tunnel. 

Although I must have missed some species due to 
limited study time, nine species of dragonflies were 
identified. Estimates of the percentage of each species, 
made mainly from the close observations of those 
perched on the walls, are in Table 1. I was able to 
confirm the presence of both males and females for 
Anax junius, Pachydiplax longipennis, Gomphaeschna 
furcillata, Erythemis simplicicollis, and Libellula 
vibrans. 


Table 1. Dragonflies recorded during fallout on 27 May 
2000 at the Chesapeake Bay Bridge-tunnel. 


Estimated 
Common Name Scientific Name % of Total 
Common Green Darner Anax junius 25 
Eastern Pondhawk Erythemis simplicicollis 25 
Harlequin Darner Gomphaeschna furcillata 10 
Blue Dasher Pachydiplax longipennis 10 
Great Blue Skimmer Libellula vibrans 10 
Swamp Darner Epiaeschna heros 10 
Halloween Pennant Celithemis eponina 5 
Eastern Amberwing Perithemis tenera 5 
Saddlebags sp. Tramea sp. <] 


I roughly estimated butterfly numbers at several 
hundred. They were common species that I am familiar 
with, however, because of the impending storm and my 
interest in the dragonflies, time was not taken to 
differentiate Clouded from Orange Sulphur nor 
Question Mark from Comma nor American Lady from 
Painted Lady. The list of butterflies identified with 
estimates of the percentage of each species seen is 
contained in Table 2. 


Table 2. Butterflies recorded during fallout on 27 May 
2000 at the Chesapeake Bay Bridge-tunnel. 


Estimated 
Common Name Scientific Name % of Total 
Clouded/Orange Colias philodice/ 25 
Sulphur C. eurytheme 
Red Admiral Vanessa atalanta 25 
Common Buckeye Junonia coenia 25 
American/Painted Vanessa virginiensis/ 10 
Lady V. cardui 
Comma/ Polygonia comma 10 
Question Mark P. interrogationis 
American Snout Libytheana carinenta 5 


On 3 June 2000, I visited the bridge-tunnel again 
and found dozens of dragonflies still present, though 
many were sluggish and could be captured by hand. I 
was able to measure and photograph several species. 
The Internet site for the North American Dragonfly 
Migration Project  (http://members.bellatlantic.net/ 
~dbarber/migrant/mig.html) described, with moving 
graphics, a “frontal boundary and radar visible 
migration” along the East Coast on 3 June 2000. 


SHORTER CONTRIBUTIONS 24 


Possible reasons for mass migrations of dragonflies 
in spring include dispersal from drought-affected areas, 
sustained southerly winds, and population increases. 
These movements may not be annual events and 
probably vary greatly in magnitude (Soltesz et al., 
1995). 


LITERATURE CITED 


Dunkle, S. W. 2000. Dragonflies Through Binoculars: 
a Field Guide to Dragonflies of North America. Oxford 
University Press, New York. 266 pp. 


Kain, T., & N. Brinkley. 1997. Chesapeake Bay 
Bridge-tunnel islands. Pp. 39-43 Jn D. W. Johnston 
(compiler). A Birder’s Guide to Virginia. American 
Birding Association, Inc., Colorado Springs, CO. 


Russell, R.W., M. L. May, K. L. Soltesz, & J. W. 
Fitzpatrick. 1998. Massive swarm migrations of 
dragonflies in eastern North America. American 
Midland Naturalist 140: 325-342. 


Soltesz, K., B. Barber, & G. Carpenter. 1995. A spring 
dragonfly migration in the Northeast. Argia 7(3): 10- 
14. 


Brian Taber 

Coastal Virginia Wildlife Observatory 
P.O. Box 912 

Eastville, Virginia 23347 


Banisteria, Number 19, 2002 
© 2002 by the Virginia Natural History Society 


RECORDS FOR WINTER SCORPIONFLIES IN 
VIRGINIA (MECOPTERA: BOREIDAE).--Although 
the great majority of mecopterans are active as adults 
during the warmer months of the year, there is a small 
and hardy contingent, species of the family Boreidae, 
which has become adapted to life during the cold winter 
periods and may even be found walking actively on 
snow. This seasonal preference has resulted in a group 
of insects somewhat less well known than. their 
thermophilus relatives, and even the details of their 
geographic distribution remain to be worked out. 
Knowledge of this family was summarized several 
decades ago (Penny, 1977) in a useful and complete 
monograph, which serves as a baseline upon which 
local studies can be superimposed. Penny recognized 
ten Nearctic species of the major genus Boreus, of 


which only two occur in the eastern states, and provided 
distributional maps which reflected the paucity of 
museum material available to him at the time. 
Although it is understandable that traditional hand- 
capture methods have not been extensively employed, 
the scarcity of Virginia records is _ surprising, 
considering that pitfall trap lines have been operated 
throughout the year at localities across the state 
including White Top Mountain. The following is a 
summary of known Virginia records based on literature 
and material in the Virginia Museum of Natural History 
(VMNH, identifications by G. W. Byers) and the 
National Museum of Natural History (USNM, 
identifications by O. S. Flint). 

Boreus brumalis (Fitch). The main body of this 
species’ range extends from Ontario and Maine west 
through Michigan and Ohio and south to the Great 
Smoky Mountains, Tennessee, with disjunct outlying 
segments in Minnesota, Wisconsin, and Illinois. There 
appear to be no published localities for the relatively 
well-collected states of Arkansas (Robison et al., 1997) 
and Kentucky (Byers & Covell, 1981). Byers (1962) 
published a record for Quantico, Prince William 
County, Virginia. Penny (1977) plotted only two 
Virginia records, including the foregoing and another in 
Giles County, presumably at or near Mountain Lake. 

New Virginia records are: Arlington’ Co.: 
Arlington, 11 December 1960, A. B. Gurney (USNM 
2). Augusta Co.: George Washington National Forest 
(GWNBP), timber management compartment 460-5, ca. 
5 mi W Stokesville, 18 May 1988, Barry D. Flamm 
(VMNH 1), same site and collector, 22 December 1988 
(VMNH 1). Shenandoah Mountain, 5 mi S Reddish 
Knob on FS Rt. 85, 17 June 1988, Kurt A. Buhlmann 
(VMNH 1); same site and collector, 19 November 1988 
(VMNH 1). Fairfax Co.: Dead Run, on snow, 20 
January 1957, A. B. Gurney (USNM 2); Falls Church, 
on snow, 18 December 1957, A. B. Gurney (USNM 1); 
River Bend Park, Great Falls, 2 January 1955, G. B. 
Vogt (USNM 1). Loudoun Co.: Appalachian Trail near 
Round Hill, 8 February 1970, O. S. Flint, Jr. (USNM 
16). Page Co.: Mountain Run, base of Strickler Knob, 
ca. 5 mi W Luray, 9 February 1975, O. S. Flint, Jr. 
(USNM 6). York Co.: Yorktown Naval Weapons 
Station, 4 April 1991, Kurt A. Buhlmann (VMNH 1). 

Most of these records are consistent with the 
known range of this boreal, psychrophilic insect. That 
for York County is a little more southward and lowland 
than might have been expected, but Prof. Byers advises 
(in litt.) that he found the species in some numbers on 
snow in Rock Creek Park, District of Columbia. 
Presumably, B. brumalis occurs in much of Virginia, 
but pitfall trapping is probably not the optimal 
technique for collecting this species. 


28 BANISTERIA 


Boreus nivoriundus (Fitch). With a range centered 
on northeastern North America, this species has been 
documented as far south as the Great Smoky 
Mountains, but not recorded for Kentucky (Byers & 
Covell, 1981) or Virginia. VMNH material is from 
Augusta Co.. ca. 5 mi W_ Stokesville, GWNF, 
compartment 453-11, 12 December 1988, Barry D. 
Flamm (VMNH 2); same site but compartment 453-1A, 
12 December 1988, Barry D. Flamm (VMNH 2). 
Nelson Co.: “The Priest”, 3900 ft., GWNF, ca. 4.5 mi 
SE Montebello, 20 January-28 February 1992, VMNH 
survey (VMNH 1). 

It is not clear why the Augusta County site should 
be favored by boreids. The substrate is upper Devonian 
red shale, with a forest cover of oak, hickory, and pine. 
Compartments 453-11 and 453-1A (B. nivoriundus) are 
both “old growth” stands which were not logged in the 
last century like the remainder of the area. 
Compartment 460-5 (B. brumalis), adjacent to 453-11, 
is currently invested in mature second growth forest, 
but generalizations cannot be drawn from so few data. 

The Virginia localities for B. nivoriundus require 
modification of the maps in Webb et al. (1975) and 
Penny (1977) to fill most of the central Appalachian 
lacuna they indicate. 

I am pleased to acknowledge the generous 
assistance, in the form of identifications, locality 
records, and manuscript review, provided by Professor 


No. 19, 2002 
George W. Byers and Dr. Oliver S. Flint, Jr. 
LITERATURE CITED 


Byers, G. W. 1962. Descriptions and distributional 
records of American Mecoptera. II. Journal of the 
Kansas Entomological Society 35: 299-307. 


Byers, G. W., & C. V. Covell, Jr. 1981. An annotated 
checklist of the scorpionflies (Mecoptera) of Kentucky. 
Entomological News 92: 196-198. 


Penny, N. D. 1977. A systematic study of the family 
Boreidae (Mecoptera). The University of Kansas 
Science Bulletin 41: 141-217. 


Robison, H. W., G. W. Byers, & C. A. Carlton. 1997. 
Annotated checklist of the Mecoptera (scorpionflies) of 
Arkansas. Entomological News 108: 313-317. 


Webb, D. W.,.N. D. Penny, & J.C. Marlin. 1975. The 
Mecoptera, or scorpionflies, of Illinois. Bulletin of the 
Illinois Natural History Survey 31: 251-316. 


Richard L. Hoffman 
Virginia Museum of Natural History 
Martinsville, Virginia 24112 


Fig. 1. Virginia localities for Boreus brumalis (@), B. nivoriundus ( &) and the site at which they are sympatric (* ). 
The extent of the Blue Ridge Physiographic Province is indicated by the two solid lines trending northeast to 


southwest. 


MISCELLANEA 29 


Miscellanea 


Reports 
1. President’s Report 


On May 11-12, 2002 a BioBlitz was conducted at 
Pocahontas State Park. Many of the members of your 
Executive Committee would have liked to offer 
financial support to this endeavor. However, given the 
current status of our finances we could not justify an 
expenditure of funds (more on this later). Nevertheless, 
the Virginia BioBlitz was supported by the participation 
of a number of VNHS members. Many of these were 
representing their respective employers but they also 
represented the contributions of the VNHS and its 
membership. Endeavors such as this require more than 
financial support and I am sure the organizers wish to 
thank each of you for your time as do I. 

Our 10" Annual Meeting was held at Hampton 
University, Hampton, Virginia on May 23, 2002. Our 
meeting was held with the Natural History and 
Biodiversity Section of the Virginia Academy of 
Science. This arrangement has greatly benefitted both 
organizations and has produced a series of successful 
meetings through the years. Thirteen oral presentations 
were given along with three posters. Six student 
presentations were in competition for the VAS William 
S. Woolcott Best Student Paper Award. 

This fall we will need to elect a new Councilor and 
a President Elect (Vice President). Joella Killian’s 
(Mary Washington College) term as Councilor expires 
in December and Barbara Abraham (Hampton 
University) will assume the office of President at the 
same time. I will be forming a nominating committee 
to come up with a slate of candidates. I also ask each of 
you to consider submitting the names of members 
willing to serve a term as a Councilor or President 
Elect. First ask the individual if they are willing to 
serve and then forward their name to me 
(wwieland@mwc.edu) or any member of the Executive 
Committee. There may also be a vote on changing the 
Bylaws regarding terms of Councilors on the same 
ballot. Currently there are three Councilors, each 
serving a 4-year term. The terms of Councilors are 
staggered to allow for an “institutional memory.” 
These criteria allow for a Councilor election each year 
with every fourth year having no election. Under this 
system it is cumbersome to keep track of terms. The 
Executive Committee is reviewing this and hopes to 
have a solution soon. 

We are half way through 2002 and with this issue 
the Virginia Natural History Society is publishing issue 
Number 19 of Banisteria. It has been an excellent 


source of information on the natural history of Virginia. 
Our current editors and the previous editor have done 
an admirable job in producing a high quality 
publication. Your governing board is, however, 
concerned about the financial stability of the VNHS. 
Subscriptions are down and our annual income from 
this source pays for the publication with little left over. 
Indeed, income from subscriptions/memberships is our 
primary means for financing this publication. Given 
the slow down in the economy we are concerned about 
our reserves for unexpected expenses. We are working 
to reduce costs while maintaining the high standard set 
by past issues of Banisteria. In short, we need to 
increase subscriptions to maintain Banisteria. A new 
VNHS brochure was prepared by councilor Tom 
McAvoy this spring. The front illustration features 
scanned covers of two past issues of Banisteria and 
should be more effective in our efforts to recruit new 
library subscriptions. Copies can be obtained from 
Anne Lund, Secretary-Treasurer. 

In one form or another I have been involved in the 
scientific community of Virginia ever since I gave my 
first presentation before the Virginia Academy of 
Science in 1972. I was absent from Virginia for a short 
period while attending graduate school. During the past 
30 odd years there has been a great proliferation of 
organizations for the study of natural history within the 
Commonwealth. Whether you joined one of these 
because of your profession or your avocation you may 
be finding yourself stretched thin. More specifically, if 
you are like me, lately you have found your pocketbook 
stretched thin. You can no longer justify a membership 
in so many groups. Unlike the Federal Government, we 
cannot have deficit spending (at least not for long) in 
our personal budget. So, you have to make a decision. 
A difficult decision, because all of these groups are 
good organizations, but there are just too many. Which 
memberships will you maintain and which must go? 
Let me give you several reasons why you should 
continue your Virginia Natural History Society 
membership. First, you get a network of like-minded 
people to share your interests. True, you could develop 
your own network but through the Society you can 
quickly come into contact with individuals it might take 
a lifetime to meet. Second, we hold an Annual Meeting 
at which members have the opportunity to 
communicate their work and also hear what others have 
found. Abstracts from these presentations are published 
in the Virginia Journal of Science. Further, student 
presenters at this meeting may compete for a $100 prize 
for best paper. Third, you receive a subscription to 
Banisteria. 


30 BANISTERIA 


Whether your area of interest is botany or zoology, 
ornithology or herpetology, ferns or thistles, or, as most 
of us, your interests are much broader when it comes to 
natural history, membership in the VNHS provides 
many benefits. The VNHS, through Banisteria, 
provides a_ significant outlet for natural history 
information on the biota of Virginia. In short, by 
maintaining a membership in the VNHS you can 
maintain a conduit to a wide and rich variety of 
Virginia naturalists. Renew your membership and tell a 
fellow naturalist! 


Respectfully submitted, 
Werner Wieland, President 


2. Secretary-Treasurer’s Report 


We have 116 memberships, 14 of which are 
institutions or libraries. These are both new and 
renewed memberships for 2002. This is not as high as 
we would like for this new year, but this is a good total 
in some ways considering that we have sent no 
additional reminders so far this year. We will be 
reminding members to renew their membership with 
the society by sending them a notice about renewal and 
a return envelope in our mailing of Banisteria (#19), 
this issue, the first for year 2002. (At the end of 2001, 
we had 158 members.) 

As always, we encourage our active members to 
recruit members for the Society. A membership form is 
included with this mailing. Pass it on to a friend or 
colleague interested in the natural history of our state. 
If you were a member last year, and have not renewed 
your membership, you are receiving this journal with a 
reminder to submit your membership payment. 

Our treasury presently holds $5,281 (as of June 11, 
2002). The expenses for the publication and mailing of 
this issue of Banisteria (#19) will be subtracted from 
this amount. We are always grateful for contributions 
from Society members above the regular membership 
amounts, and we have received thirteen such donations 
during the first half of the year totaling $175. 

An important item to mention in our treasury report 
is that the Society provided a graduate fellowship of 
$500 for a young biologist to work at the Virginia 
Museum of Natural History in Martinsville, Virginia. 

We continue to be grateful to Hampden-Sydney 
College for support with the paperwork concerning our 
treasury. The secretary at Gilmer Hall, Hampden- 
Sydney College, Beckie Smith, has done a great job of 
keeping our records of membership, and she has 
prepared the address labels for all mailings. We thank 


No. 19, 2002 


her for her dedication to these tasks, and we thank the 
College for supplying this support to the Society. 

Please submit all enquiries about membership in the 
Society or about past issues of Banisteria to: Dr. Anne 
Lund, Virginia Natural History Society, Box 62, 
Hampden-Sydney, Virginia 23943. 


Respectfully submitted, 
Anne Lund, Secretary/Treasurer 


3. Editors’ Report 
Personal Commentary I 


I am glad to see that my Personal Commentary in 
Banisteria 18 generated some responses. I want to say 
at the outset here that I apologize to anyone who took 
offense. I grew increasingly tired of saying the same 
old thing in each issue - "We need more manuscripts." 
This is a common problem with small journals, 
although the breadth of ours should allow for authors of 
many disciplines to make plenty of contributions. My 
commentary was written to analyze why so few 
manuscripts were submitted and to see if I could 
wrench out a few from people who had just not taken 
the time to finish one. 

In the context of the commentary, laziness was 
equated with how one arranges his or her priorities. I 
have decided a long time ago to put publications high 
on my list of priorities. Others may value teaching or 
other professional pursuits somewhat more. I certainly 
don't believe anyone out there is lazy, as we are all 
working harder than ever. Maybe I cannot expect 
others to value publishing one's natural history 
information or data as much as I do. I simply remain 
concerned that we are not seeing the number of 
submissions that will ensure that Banisteria will thrive. 

I truly believe in the concept of teamwork. Effective 
team players are leaders when they need to be and 
followers when they need to be. Team players support 
the goal of the team. The VNHS team has a primary 
goal of publishing Banisteria. This goal is achieved 
only if the team players contribute to it. Thus, the 
success of the team, in this case the success of 
Banisteria, is realized by those members who 
contribute manuscripts. I wish that all of you were 
contributing members of this team. Some members 
contribute in other important ways, such as serving as 
society officers. However important this service is, the 
success of our journal is_ still dependent on 
contributions from the team. 


MISCELLANEA 31 


So, again, I apologize to any reader that had 
problems with my previous commentary. The rest of 
you saw though the ruse for what it was, a tactic to 
generate more manuscripts for Banisteria and, 
admittedly, for venting some frustration over this issue. 


Joe Mitchell 


The Spring 2002 issue of Banisteria (Number 19) 
will be smaller than many previous issues. This is due 
entirely to the fact that manuscript submissions have 
been slow in coming. We have several in the review 
process that should make the next issue full size. 
Remember to send _ vertebrate and biography 
manuscripts to Joe Mitchell and those on invertebrates 
and plants to Steve Roble. 


Joe Mitchell and Steve Roble, Co-editors 


4. Tenth Annual Meeting of the Virginia Natural 
History Society 


The 10“ annual meeting of the VNHS was held on 23 
May 2002 at Hampton University, Hampton, VA. The 
titles of papers presented at this meeting are listed 
below: 


Microhabitat differences between the ants Monomorium 
minimum and M. viride (Formicidae: Myrmicinae) in a 
longleaf pine forest. H. C. Revis and D. A. Waller. 


A demographic analysis of the snail Leptoxis carinata 
in an Appomattox River tributary: movement patterns 
vary as a function of habitat type. L. M. Brantley, T. R. 
Edwards, and T. W. Stewart. 


Colony distribution of the fungus-growing ant 
Trachymyrmex  septentrionalis related to _ light 
availability in a longleaf pine habitat. J. P. Howell and 
D. A. Waller. 


Den tree and habitat characteristics of the northern 
flying squirrel (Glaucomys sabrinus) in two different 
aged stands in the Mt. Rogers NRA. M. Hackett and 
J. Pagels. 


Trends through time: 57 years of spring arrival dates 
of Neotropical migrant birds in central Virginia. 
P. Bedell. 


Assessment of biological integrity in an agriculturally 
impacted Virginia mountain stream. J. H. Roberts, T. J. 
Newcomb, and M. J. Pinder. 


Ant catch related to pitfall trap type in a longleaf pine 
habitat. D. A. Waller. 


Life history aspects of the creeper, Strophitus 
undulatus, and green floater, Lasmigona_ subviridis 
(Bivalvia: Unionidae). R. A. Mair, J. W. Jones, and 
R. J. Neves. 


Using zebrafish 
pollutants in sediments of Virginia waters. 
Northington and T. W. Stewart. 


survivorship to monitor organic 
R. M. 


Effect of prescribed burns on insect diversity in a 
longleaf pine habitat. C. F. Abadam and D. A. Waller. 


Subterranean termite (Isoptera: Rhinotermitidae) 
response to essential oils. L. K. Baron and D. A. 
Waller. 


Distribution of the endangered Roanoke logperch, 
Percina rex, and species of concern Roanoke bass, 
Ambloplites cavifrons, within the Smith River drainage. 
T. Smith. 


Anuran oviposition site selection: how behavior 
influences community structure. J. F. Rieger, C. A. 
Binckley, and W. J. Resetarits, Jr. 


The following posters also were presented at the 
meeting: 


An unusual coat color pattern in a short-tailed shrew, 
Blarina brevicauda. G. B. Bumann and P. F. Scanlon. 


Habitat use and exploitation of the striped bass and 
hybrid striped bass in Claytor Lake, Virginia: 
preliminary findings. J. M. Kilpatrick and J. J. Ney. 


Phylogeography of raccoons (Procyon lotor) on the 
Virginia barrier islands: a nested clade analysis of 
mitochondrial DNA haplotypes. N. D. Moncrief, R. A. 
Van Den Bussche, and R. D. Dueser. 


Announcements 


1. Flora of Virginia Project 


For more than half a century, Virginia botanists 
have attempted to develop a Flora of Virginia. 
Through a coalition of public, academic, and private 
cooperators, this elusive dream may soon become 
reality. In 2001, the non-profit organization, The 
Foundation of the Flora of Virginia Project, Inc. was 


32, BANISTERIA 


founded with the ambitious goal of completing an 
illustrated manual with accompanying illustrated 
website by the year 2007. 

Chris Ludwig, Chief Biologist of the Virginia 
Division of Natural Heritage, heads the Foundation as 
Executive Director and Board President. Other Board 
members include Dr. Donna Ware, former curator of 
the College of William and Mary herbarium and a 
coauthor of the Atlas of the Virginia Flora; Michael 
Lipford, Vice President and Virginia Executive 
Director of The Nature Conservancy; Nicky Staunton, 
President of the Virginia Native Plant Society; Dr. Chip 
Morgan, representative of the Wintergreen Nature 
Foundation; Marion Lobstein, Vice President of the 
Virginia Academy of Science; Tom Smith, director of 
the Virginia Division of Natural Heritage, and Mike 
Garson, the Foundation’s attorney. Dr. Rex Baird, chair 
of the Virginia Academy of Science Flora Committee, 
is Treasurer. 

The Flora of Virginia will be written by Alan 
Weakley, curator of the University of North Carolina 
Herbarium and Chris Ludwig, who was Botanist with 
Virginia Natural Heritage. Other contributors and 
authors will be involved as well. The authors are co- 
chairs of a 40-member technical advisory board that 
includes many of Virginia’s finest botanists. The 
advisory board will assist in key decisions on content 
and format and provide crucial technical assistance to 
the Project such as field testing keys and descriptions, 
providing materials for illustrators, and _ possibly 
providing portions of the manual and website’s text. 

This effort requires solid financial backing. Joslin 
Gallatin, past-president and fundraiser for the 
Foundation of the State Arboretum, is the Project’s 
fundraiser. The Project has also been bolstered by a 
sizable donation from the Virginia Division of Natural 
Heritage. The Project has initiated other fundraising 
efforts through major grant applications and requests 
from private individuals. To learn more about the Flora 
of Virginia Project, visit the project website at 
www.dcr.state.va.us/dnh/vaflora.htm. 


Instructions for Contributors 


Banisteria accepts manuscripts that contribute to the 
public and scientific knowledge of the natural history of 
Virginia. This publication is intended to be an outlet for 
the kind of information that is useful but would not be 
accepted in the mainstream journals. Information found 
in field notebooks and files that never made it into 
scientific journals is especially important. Manuscripts 
derived from natural history observations, small-scale 


No. 19, 2002 


field projects, distribution surveys and reviews, species 
inventories, reports for contracted environmental 
projects, and unpublished theses are especially desired. 
The focus of Banisteria is classical and_ therefore 
slanted toward organismal biology. Reviews of books 
relevant to Virginia’s natural history and biographies of 
naturalists influential in this field are also welcomed by 
the editors. The journal also is suited for papers on the 
history of natural history as it pertains to Virginia. 

To qualify for publication in Banisteria, the 
manuscript must pertain in some way to the flora, 
fauna, geology, geography or Native Americans of the 
Commonwealth. Papers focusing largely on projects 
conducted outside of the state will be considered only if 
there is a strong connection to Virginia. Papers may be 
full length or shorter contributions, and we are always 
looking for book reviews. Authors are not required to 
be members of the Virginia Natural History Society to 
submit manuscripts, although membership in VNHS is 
strongly encouraged. There are no page charges for 
members. The editors will be happy to assist authors in 
their preparation of manuscripts. We would rather help 
get natural history information published for others to 
use than have it remain on the shelf or in someone's 
desk. 

Manuscripts on vertebrates, history, biography, and 
material for the Miscellanea section (book reviews, 
announcements, news of members, obituaries, etc.) 
should be sent to Joe Mitchell. Manuscripts on plants 
and invertebrates should be sent to Steve Roble. Papers 
on other topics can be submitted to either editor. 
Mitchell and Roble will serve as editors for each other's 
papers and an associate editor will be asked to serve as 
editor for those papers written jointly by the co-editors. 

Manuscripts should be sent in duplicate to the 
appropriate co-editor (see previous paragraph), who 
will in turn seek one or two reviews. Authors should 
retain both the original typescript and figures until final 
acceptance for publication. Photocopies are adequate 
for review purposes. 

Manuscripts must be written on one side of standard 
size paper (21.5 x 28 cm) using double spacing 
throughout. Words should not be hyphenated. 
Manuscripts should be arranged in the following order: 
title, author’s name, author’s address, text, 
acknowledgments, literature cited, tables, figure 
legends, figures. Long manuscripts should have 
standard sections, e.g., Materials and Methods, Results, 
and Discussion, although some papers may not be 
amenable to such division, and short manuscripts (<4-6 
pages) need not have these sections. All pages should 
be numbered, including tables. The title should be 
concise but informative. It and the author’s name and 


MISCELLANEA 33 


address should be centered at the top of the first page. 
The text should begin on the first page beneath the 
author’s address. Use good judgment on arrangement of 
sections when other than the standard approach is 
necessary. Use italics or underlines for species’ 
scientific names. 


References: Use the following as a guide. Do not 
abbreviate journal names. 


Journal article with I author: 

Scott, D. 1986. Notes on the eastern hognose snake, 
Heterodon platyrhinos Latreille (Squamata: 
Colubridae), in a Virginia barrier island. Brimleyana 
12: 51-55. 


Journal article with 2 authors: 

Tilley, S. C., & D. W. Tinkle. 1968. A reinterpretation 
of the reproductive cycle and demography of the 
salamander Desmognathus ochrophaeus. Copeia 1968: 
299-303. 


Journal article with 3+ authors: 

Funderburg, J. B., P. Hertz, & W. M. Kerfoot. 1974. A 
range extension for the carpenter frog, Rana virgatipes 
Cope, in the Chesapeake Bay region. Bulletin of the 
Maryland Herpetological Society 10: 77-79. 


Book: 
Harris, L. D. 1984. The Fragmented Forest. University 
of Chicago Press, Chicago, IL. 211 pp. 


Chapter in a book: 

Gentry, A. H. 1986. Endemism in tropical versus 
temperate plant communities. Pp. 153-181 Jn M. Soule 
(ed.), Conservation Biology. Sinauer Associates, Inc., 
Sunderland, MA. 


Report: 
The Nature Conservancy. 1975. The preservation of 
natural diversity: A survey and recommendations. 
Report to the U.S. Department of Interior, Washington, 
DC. 189 pp. (include report series and number if 
present). 


Thesis: 
Riddick, M. B. 1973. Freshwater mussels of the 
Pamunkey River system, Virginia. Master’s Thesis, 
Virginia Commonwealth University, Richmond, VA. 
105 pp. 


Tables: Each table should be typed on a separate sheet 
of paper, preferably using 10 point font. A legend for 


each table should follow the number and must be on the 
same page as the table. Ruled, horizontal lines should 
be avoided except at the top and bottom of the table. 
Remember that each table must fit within a space of 
6.5 x 8.5 inches, and that reduction may cause loss of 
detail. 


Figures: Black and white line drawings are acceptable 
for publication. They should be no more than twice the 
size of final publication size, and if several are 
assembled as a plate, keep the ratio of height to width 
consistent with the rectangular shape of the page. 
The back of each figure should be labeled with the 
author’s name. 


Photographs: Banisteria will accept high contrast 
black and white photographs. Submit at least 5 x 7 inch 
(12.5 x 17.5 cm) photos and mount them if possible. 
Remember that reduction to fit column or page width 
will cause loss of detail. 


Abbreviations: The following common abbreviations 
are accepted in Banisteria: n (sample size), no. 
(number), SVL (snout-vent length; define on first 
usage), DBH (diameter at breast height), yr (years), mo 
(months), wk (weeks), h (hours), min (minutes), 
s (seconds), P (probability), df (degrees of freedom), 
SD and SE (standard deviation and standard error), 
ns (not significant), | (liter), g (gram), mm (millimeter), 
m (meter), km (kilometer), and C (degrees Celsius). 
Do not abbreviate “male” and “female”, or dates, or 
undefined terms. 


Electronic transfer of manuscripts: After a 
manuscript has been accepted for publication, one paper 
copy and an electronic copy on a 3.5 inch diskette 
should be sent to S. M. Roble. If possible, use IBM- 
compatible systems with Microsoft Word or Word 
Perfect. Please do not justify right-hand margins, and 
do not attempt to produce “camera-ready copy.” 


Reprints: Reprints are not provided. However, authors 
will be sent one printed copy of their formatted article 
to allow them or their institutions to prepare 
photocopies or electronic files for personal use or 
exchange purposes. 


Page charges: Page charges are waived for 
manuscripts written or coauthored by members of the 
Virginia Natural History Society, although members 
with grant funds are encouraged to contribute toward 
printing costs. Nonmember authors will be accessed 
page charges at a rate of $10 per printed page. 


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